Approval of Air Quality Implementation Plans; California; Ventura County; 8-Hour Ozone Nonattainment Area Requirements, 70109-70130 [2019-27545]
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Federal Register / Vol. 84, No. 245 / Friday, December 20, 2019 / Proposed Rules
oxides would not exceed the following
maximum allowable increases over
minor source baseline concentration for
such pollutants:
(6) Sulfur dioxide variance by
Governor with Federal Land Manager’s
concurrence. The owner or operator of
a proposed source or modification
which cannot be approved under
paragraph (p)(5) of this section may
demonstrate to the Governor that the
source cannot be constructed by reason
of any maximum allowable increase for
sulfur dioxide for a period of 24 hours
or less applicable to any Class I area
and, in the case of Federal mandatory
Class I areas, that a variance under this
clause would not adversely affect the air
quality related values of the area
(including visibility). The Governor,
after consideration of the Federal Land
Manager’s recommendation (if any) and
subject to his concurrence, may, after
notice and public hearing, grant a
variance from such maximum allowable
increase. If such variance is granted, the
Administrator shall issue a permit to
such source or modification pursuant to
the requirements of paragraph (p)(8) of
this section provided that the applicable
requirements of this section are
otherwise met.
(7) Variance by the Governor with the
President’s concurrence. In any case
where the Governor recommends a
variance with which the Federal Land
Manager does not concur, the
recommendations of the Governor and
the Federal Land Manager shall be
transmitted to the President. The
President may approve the Governor’s
recommendation if he finds that the
variance is in the national interest. If the
variance is approved, the Administrator
shall issue a permit pursuant to the
requirements of paragraph (p)(8) of this
section provided that the applicable
requirements of this section are
otherwise met.
(8) Emission limitations for
Presidential or gubernatorial variance.
In the case of a permit issued pursuant
to paragraph (p)(6) or (7) of this section,
the source or modification shall comply
with such emission limitations as may
be necessary to assure that emissions of
sulfur dioxide from the source or
modification would not (during any day
on which the otherwise applicable
maximum allowable increases are
exceeded) cause or contribute to
concentrations which would exceed the
following maximum allowable increases
over the baseline concentration and to
assure that such emissions would not
cause or contribute to concentrations
which exceed the otherwise applicable
maximum allowable increases for
periods of exposure of 24 hours or less
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for more than 18 days, not necessarily
consecutive, during any annual period:
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(r) * * *
(4) At such time that a particular
source or modification becomes a major
stationary source or major modification
solely by virtue of a relaxation in any
enforceable limitation which was
established after August 7, 1980, on the
capacity of the source or modification
otherwise to emit a pollutant, such as a
restriction on hours of operation, then
the requirements of paragraphs (j)
through (s) of this section shall apply to
the source or modification as though
construction had not yet commenced on
the source or modification.
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(u) * * *
(2) * * *
(i) * * *
(ii) The delegate agency shall send a
copy of any public comment notice
required under paragraph (q) of this
section to the Administrator through the
appropriate Regional Office.
(3) In the case of a source or
modification which proposes to
construct in a Class III area, emissions
from which would cause or contribute
to air quality exceeding the maximum
allowable increase applicable if the area
were designated a Class III area, and
where no standard under section 111 of
the Act has been promulgated for such
source category, the Administrator must
approve the determination of best
available control technology as set forth
in the permit.
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(w) Permit rescission. (1) Any permit
issued under this section or a prior
version of this section shall remain in
effect, unless and until it expires under
paragraph (r)(2) of this section or is
rescinded under this paragraph (w).
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[FR Doc. 2019–25973 Filed 12–19–19; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R09–OAR–2018–0146; FRL–10003–
39–Region 9]
Approval of Air Quality Implementation
Plans; California; Ventura County; 8Hour Ozone Nonattainment Area
Requirements
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
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70109
The Environmental Protection
Agency (EPA) is proposing to approve,
or conditionally approve, all or portions
of two state implementation plan (SIP)
revisions submitted by the State of
California to meet Clean Air Act (CAA
or ‘‘the Act’’) requirements for the 2008
8-hour ozone national ambient air
quality standards (NAAQS or
‘‘standards’’) in the Ventura County,
California (‘‘Ventura County’’) ozone
nonattainment area. The two SIP
revisions include the ‘‘Final 2016
Ventura County Air Quality
Management Plan,’’ and the Ventura
County portion of the ‘‘2018 Updates to
the California State Implementation
Plan.’’ In today’s action, the EPA refers
to these submittals collectively as the
‘‘2016 Ventura County Ozone SIP.’’ The
2016 Ventura County Ozone SIP
addresses the nonattainment area
requirements for the 2008 ozone
NAAQS, including the requirements for
an emissions inventory, attainment
demonstration, reasonable further
progress, reasonably available control
measures, contingency measures, among
others; and establishes motor vehicle
emissions budgets. The EPA is
proposing to approve the 2016 Ventura
County Ozone SIP as meeting all the
applicable ozone nonattainment area
requirements except for the contingency
measure requirement, for which the
EPA is proposing conditional approval.
In addition, the EPA is beginning the
adequacy process for the 2020 motor
vehicle emissions budgets in the 2016
Ventura County Air Quality
Management Plan through this proposed
rule.
DATES: Written comments must arrive
on or before January 21, 2020.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R09–
OAR–2018–0146 at https://
www.regulations.gov. For comments
submitted at Regulations.gov, follow the
online instructions for submitting
comments. Once submitted, comments
cannot be edited or removed from
Regulations.gov. The EPA may publish
any comment received to its public
docket. Do not submit electronically any
information you consider to be
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Multimedia
submissions (audio, video, etc.) must be
accompanied by a written comment.
The written comment is considered the
official comment and should include
discussion of all points you wish to
make. The EPA will generally not
consider comments or comment
contents located outside of the primary
submission (i.e., on the web, cloud, or
SUMMARY:
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other file sharing system). For
additional submission methods, please
contact the person identified in the FOR
FURTHER INFORMATION CONTACT section.
For the full EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www.epa.gov/dockets/
commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT: John
Kelly, Air Planning Office (AIR–2), EPA
Region IX, 75 Hawthorne Street, San
Francisco, CA 94105, (415) 947–4151, or
by email at kelly.johnj@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we,’’ ‘‘us,’’
and ‘‘our’’ refer to the EPA.
Table of Contents
I. Regulatory Context
A. Ozone Standards, Area Designations,
and SIPs
B. The Ventura County Ozone
Nonattainment Area
C. CAA and Regulatory Requirements for
2008 Ozone Nonattainment Area SIPs
II. Submissions From the State of California
To Address 2008 Ozone Requirements in
Ventura County
A. Summary of Submissions
B. CAA Procedural Requirements for
Adoption and Submission of SIP
Revisions
III. Evaluation of the 2016 Ventura County
Ozone SIP
A. Emissions Inventories
B. Emissions Statement
C. Reasonably Available Control Measures
Demonstration
D. Attainment Demonstration
E. Rate of Progress Plan and Reasonable
Further Progress Demonstration
F. Contingency Measures
G. Motor Vehicle Emissions Budgets for
Transportation Conformity
H. General Conformity Budgets
I. Other Clean Air Act Requirements
Applicable to Serious Ozone
Nonattainment Areas
IV. Proposed Action
V. Statutory and Executive Order Reviews
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I. Regulatory Context
A. Ozone Standards, Area Designations,
and SIPs
Ground-level ozone pollution is
formed from the reaction of volatile
organic compounds (VOC) and oxides of
nitrogen (NOX) in the presence of
sunlight.1 These two pollutants, referred
to as ozone precursors, are emitted by
many types of sources, including onand off-road motor vehicles and
engines, power plants and industrial
1 The
State of California refers to reactive organic
gases (ROG) rather than VOC in some of its ozonerelated SIP submissions. As a practical matter, ROG
and VOC refer to the same set of chemical
constituents, and for the sake of simplicity, we refer
to this set of gases as VOC in this proposed rule.
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facilities, and smaller area sources such
as lawn and garden equipment and
paints.
Scientific evidence indicates that
adverse public health effects occur
following exposure to ozone,
particularly in children and adults with
lung disease. Breathing air containing
ozone can reduce lung function and
inflame airways, which can increase
respiratory symptoms and aggravate
asthma or other lung diseases.2
Under section 109 of the CAA, the
EPA promulgates NAAQS for pervasive
air pollutants, such as ozone. The
NAAQS are concentration levels that,
the attainment and maintenance of
which, the EPA has determined to be
requisite to protect public health and
welfare. In 1979, the EPA established
the 1-hour ozone NAAQS of 0.12 parts
per million (ppm) (referred to herein as
the ‘‘1-hour ozone NAAQS’’).3 Section
110 of the CAA requires states to
develop and submit SIPs to implement,
maintain, and enforce the NAAQS.
Under the CAA, as amended in 1977,
the EPA designated all areas of the
country as ‘‘nonattainment,’’
‘‘attainment,’’ or ‘‘unclassifiable’’ with
respect to each NAAQS, and in so
doing, designated Ventura County
(excluding the Channel Islands) as a
nonattainment area for photochemical
oxidant (later ozone).4 States with
nonattainment areas are required to
submit revisions to their SIPs that
include a control strategy and technical
analysis to demonstrate how the area
will attain the NAAQS (referred to as an
‘‘attainment demonstration’’), and the
EPA took action on a number of related
SIP revisions submitted by the
California Air Resources Board (CARB)
in the late 1970s and 1980s for Ventura
County.5 Under the 1977 CAA
Amendments, nonattainment areas were
2 ‘‘Fact Sheet—2008 Final Revisions to the
National Ambient Air Quality Standards for
Ozone,’’ dated March 2008.
3 44 FR 8202 (February 8, 1979).
4 43 FR 8962, at 8972 (March 3, 1978). Ventura
County lies within California’s South Central Coast
Air Basin, which includes the counties of Santa
Barbara and San Luis Obispo in addition to Ventura
County.
5 Under California law, CARB is the state agency
that is responsible for the adoption and submission
to the EPA of California SIPs and SIP revisions, and
it has broad authority to establish emissions
standards and other requirements for mobile
sources. Local and regional air pollution control
districts in California are responsible for the
regulation of stationary sources and are generally
responsible for the development of regional air
quality plans. In Ventura County, the Ventura
County Air Pollution Control District develops and
adopts air quality management plans to address
CAA planning requirements applicable to that
region. Such plans are then submitted to CARB for
adoption and submittal to the EPA as revisions to
the California SIP.
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to have attained the 1-hour ozone
NAAQS no later than 1987. By 1990,
however, like many other areas
throughout the country, Ventura County
had not yet attained the 1-hour ozone
NAAQS, and the CAA was amended to
include new SIP requirements and new
attainment deadlines.
Under the CAA Amendments of 1990,
Ventura County (excluding the Channel
Islands) was classified as a ‘‘Severe-15’’
nonattainment area for the 1-hour ozone
NAAQS based on a 1-hour ozone design
value of 0.17 parts per million (ppm).6
As a Severe-15 ozone nonattainment
area, Ventura County was required to
attain the 1-hour ozone NAAQS no later
than November 15, 2005 and was
subject to additional SIP planning
requirements, including a revised
attainment demonstration.
In the wake of the classification of
Ventura County as a Severe-15
nonattainment area for the 1-hour ozone
NAAQS, CARB submitted a number of
SIP revisions for Ventura County that
contained an attainment demonstration
for the 1-hour ozone NAAQS and other
SIP elements, and that relied on a
combination of mobile source control
measures adopted by CARB and
stationary source control measures
adopted by the Ventura County Air
Pollution Control District (VCAPCD or
‘‘District’’). In connection with these
submittals, the EPA took the following
actions:
• 1994 Air Quality Management Plan
for Ventura County and related State
Strategy—The EPA approved the control
measures, the 15 percent rate of progress
demonstration and attainment
demonstration, among other elements,
for the 1-hour ozone NAAQS at 62 FR
1150 (January 8, 1997);
• Ventura County 1995 Air Quality
Management Plan Revision—The EPA
approved the revised rule adoption and
implementation schedule at 62 FR 1150
(January 8, 1997);
• Ventura County 1997 Air Quality
Management Plan—The EPA approved
certain commitments to adopt and
implement control measures at 63 FR
19659 (April 21, 1998).
As noted previously, Ventura County
was required to attain the 1-hour ozone
NAAQS no later than 2005, and in 2009,
the EPA determined that Ventura
County had attained the 1-hour ozone
NAAQS by the 2005 applicable
attainment date.7 Since 2005, 1-hour
6 56 FR 56694 (November 6, 1991). For the 1-hour
ozone NAAQS, the Channel Islands of Ventura
County are part of the unclassifiable/attainment
area comprised by the Channel Islands portion of
the South Central Coast Air Basin. See 56 FR 56694,
at 56732 (November 6, 1991).
7 74 FR 25153 (May 27, 2009).
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ozone design values in Ventura County
have decreased from 0.12 ppm in 2005
(based on 2003–2005 data) to 0.10 ppm
in 2018 (based on 2016–2018 data) and
are consistent with continued
attainment of the 1-hour ozone
NAAQS.8
In 1997, the EPA revised the NAAQS
for ozone, setting it at 0.08 ppm
averaged over an 8-hour timeframe
(referred to herein as the ‘‘1997 ozone
NAAQS’’) to replace the existing 1-hour
ozone NAAQS of 0.12 ppm.9 In 2004,
the EPA designated and classified
Ventura County (excluding the Channel
Islands) as a ‘‘Moderate’’ nonattainment
area for the 1997 ozone NAAQS but
later granted CARB’s request to
reclassify Ventura County to ‘‘Serious’’
nonattainment for the 1997 ozone
NAAQS.10 Serious ozone nonattainment
areas were required to attain the 1997
ozone NAAQS as expeditiously as
practicable, but no later than June 15,
2013. In 2012, the EPA determined that
Ventura County attained the 1997 ozone
NAAQS based on the ambient data for
years 2009–2011.11 Since 2011, the
eight-hour ozone design values for
Ventura County have decreased from
0.083 ppm in 2011 (based on 2009–2011
data) to 0.078 ppm in 2018 (based on
2016–2018 data) and are consistent with
continued attainment of the 1997 ozone
NAAQS.12
In 2008, the EPA lowered the 8-hour
ozone NAAQS to 0.075 ppm (referred to
herein as the ‘‘2008 ozone NAAQS’’) to
replace the 1997 ozone NAAQS of 0.08
8 Under EPA regulations at 40 CFR 50.9 and
appendix H, the 1-hour ozone NAAQS is attained
at a site when the expected number of days per
calendar year with maximum hourly average
concentrations above 0.12 ppm is equal to or less
than 1. The design value for 1-hour ozone is
generally the fourth highest daily maximum 1-hour
ozone concentration measured during a 3-year
period at each site in the area, assuming 3 complete
years of data. The highest design value among the
various ozone monitoring sites represents the
design value for the area. The data for Ventura
County is from CARB, Aerometric Data Analysis
System Air Quality Database, Ventura County
Ozone Trends Summary Report, September 11,
2019.
9 62 FR 38856 (July 18, 1997).
10 69 FR 23857 at 23889 (April 30, 2004); 73 FR
29073 (May 20, 2008).
11 77 FR 56775 (September 14, 2012).
12 Under EPA regulations at 40 CFR 50.10 and
appendix I, the 1997 ozone NAAQS is attained at
a site when the 3-year average of the annual fourthhighest daily maximum 8-hour average ozone
concentration is less than or equal to 0.08 ppm.
This 3-year average is referred to as the design
value. When the design value is less than or equal
to 0.084 ppm (based on the rounding convention in
40 CFR part 50, appendix I) at each monitoring site
within the area, then the area is meeting the 1997
ozone NAAQS. The highest design value among the
various ozone monitoring sites in the area
represents the design value for the area. The data
for Ventura County is from EPA, Design Value
Report, dated July 3, 2019.
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ppm.13 In 2012, the EPA designated
Ventura County (excluding the Channel
Islands) as nonattainment for the 2008
ozone NAAQS and classified the area as
Serious.14 Areas classified as Serious
must attain the NAAQS within 9 years
of the effective date of the
nonattainment designation.15 The SIP
revisions that are the subject of today’s
proposed action address the Serious
nonattainment area requirements that
apply to Ventura County for the 2008
ozone NAAQS.
B. The Ventura County Ozone
Nonattainment Area
The Ventura County nonattainment
area for the 2008 ozone NAAQS consists
of the Ventura County portion of
California’s South Central Coast Air
Basin, excluding the Channel Islands.
Ventura County encompasses
approximately 2,200 square miles and
has a population of approximately
874,000 (in 2018); it is located west of
Los Angeles County and is bordered by
Kern County to the north, Santa Barbara
County and the Pacific Ocean to the
west, and the Pacific Ocean and Los
Angeles County to the south. Ozone in
the Ventura County nonattainment area
is caused by both locally generated
emissions and transport from the South
Coast Air Basin.16 Ocean-going vessels
calling on Port Hueneme or the ports of
Los Angeles or Long Beach and
transiting vessels passing through
southern California waters, but without
calling at the ports, also impact Ventura
County’s air quality.
C. CAA and Regulatory Requirements
for 2008 Ozone Nonattainment Area
SIPs
States must implement the 2008
ozone NAAQS under title I, part D of
the CAA, including sections 171–179B
of subpart 1 (‘‘Nonattainment Areas in
General’’) and sections 181–185 of
subpart 2 (‘‘Additional Provisions for
Ozone Nonattainment Areas’’). To assist
states in developing effective plans to
address ozone nonattainment problems,
in 2015, the EPA issued a SIP
Requirements Rule (SRR) for the 2008
ozone NAAQS (‘‘2008 Ozone SRR’’) that
addressed implementation of the 2008
13 73 FR 16436 (March 27, 2008). The EPA further
tightened the 8-hour ozone NAAQS to 0.070 ppm
in 2015, but this proposed action relates to the
requirements for the 2008 ozone NAAQS.
Information on the 2015 ozone NAAQS is available
at 80 FR 65292 (October 26, 2015).
14 77 FR 30088 (May 21, 2012).
15 CAA section 181(a)(1), 40 CFR 51.1102 and
51.1103(a).
16 The South Coast Air Basin includes Orange
County, the southwestern two-thirds of Los Angeles
County, southwestern San Bernardino County, and
western Riverside County.
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70111
standards, including attainment dates,
requirements for emissions inventories,
attainment and reasonable further
progress (RFP) demonstrations, among
other SIP elements, as well as the
transition from the 1997 ozone NAAQS
to the 2008 ozone NAAQS and
associated anti-backsliding
requirements.17 The 2008 Ozone SRR is
codified at 40 CFR part 51, subpart AA.
We discuss the CAA and regulatory
requirements for the elements of 2008
ozone plans relevant to this proposal in
more detail below.
The EPA’s 2008 Ozone SRR was
challenged, and on February 16, 2018,
the U.S. Court of Appeals for the D.C.
Circuit (‘‘D.C. Circuit’’) published its
decision in South Coast Air Quality
Management District v. EPA18 (‘‘South
Coast II’’) 19 vacating portions of the
2008 Ozone SRR. The only aspect of the
South Coast II decision that affects this
proposed action is the vacatur of the
alternative baseline year for RFP plans.
More specifically, the 2008 Ozone SRR
required states to develop the baseline
emissions inventory for RFP plans using
the emissions for the most recent
calendar year for which states submit a
triennial inventory to the EPA under
subpart A (‘‘Air Emissions Reporting
Requirements’’) of 40 CFR part 51,
which was 2011. However, the 2008
Ozone SRR allowed states to use an
alternative year, between 2008 and
2012, for the baseline emissions
inventory provided that the state
demonstrated why the alternative
baseline year was appropriate. In the
South Coast II decision, the D.C. Circuit
vacated the provisions of the 2008
Ozone SRR that allowed states to use an
alternative baseline year for
demonstrating RFP.
II. Submissions From the State of
California To Address 2008 Ozone
Requirements in Ventura County
A. Summary of Submissions
In this document, we are proposing
action on all or portions of two SIP
revisions, which are described in detail
in the following paragraphs.
Collectively, we refer to the relevant
portions of the two SIP revisions as the
2016 Ventura County Ozone SIP.
17 80
FR 12264 (March 6, 2015).
Coast Air Quality Management District v.
EPA, 882 F.3d 1138 (D.C. Cir. 2018) (‘‘South Coast
II’’).
19 The term ‘‘South Coast II’’ is used in reference
to the 2018 court decision to distinguish it from a
decision published in 2006 also referred to as
‘‘South Coast.’’ The earlier decision involved a
challenge to the EPA’s Phase 1 implementation rule
for the 1997 ozone NAAQS. South Coast Air
Quality Management Dist. v. EPA, 472 F.3d 882
(D.C. Cir. 2006).
18 South
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1. VCAPCD’s 2016 Air Quality
Management Plan
On April 11, 2017, CARB submitted
the Final 2016 Ventura County Air
Quality Management Plan (February 14,
2017) (‘‘2016 Ventura County AQMP’’)
to the EPA as a revision to the California
SIP.20 The 2016 Ventura County AQMP
addresses the nonattainment area
requirements for Ventura County for the
2008 ozone NAAQS.
More specifically, the 2016 Ventura
County AQMP includes a base year
emissions inventory,21 reasonably
available control measure (RACM)
demonstration, RFP demonstration,
attainment demonstration, contingency
measures, motor vehicle and general
conformity emissions budgets, and it
also addresses the emissions statement
requirement. The appendices to the
2016 Ventura County AQMP provide
documentation for the emissions
inventories, RACM demonstration, and
the photochemical modeling conducted
in support of the attainment
demonstration. Further support for the
attainment demonstration is provided in
Appendix J (‘‘Ventura County
Unmonitored Area Analysis’’) and
Appendix K (‘‘Ventura County Weight
of Evidence Assessment’’). The April 11,
2017 SIP submittal of the 2016 Ventura
County AQMP was accompanied by
public process documentation at both
the County and State levels.
Since submittal of the 2016 Ventura
County AQMP, CARB has replaced or
supplemented certain elements of the
2016 Ventura County AQMP (such as
the RFP demonstration and contingency
measure element) through a SIP revision
20 Letter dated April 11, 2017, from Richard W.
Corey, Executive Officer, CARB, to Alexis Strauss,
Acting Regional Administrator, EPA Region IX.
21 The 2012 base year emissions inventory
included in the 2016 Ventura County AQMP
supersedes and replaces a previous submittal of the
2012 base year emissions inventory for Ventura
County in the ‘‘8-Hour Ozone State Implementation
Plan Emission Inventory Submittal’’ (the ‘‘MultiArea Emission Inventory’’). The Multi-Area
Emission Inventory was submitted by CARB on July
17, 2014, and included 2012 base year emissions
inventories for 16 nonattainment areas, including
Ventura County. Relative to the corresponding
inventory for Ventura County in the Multi-Area
Emission Inventory, the 2012 base year emissions
inventory in the 2016 Ventura County AQMP
reflects updated stationary, area, and nonroad
source calculations as well as an updated version
of the EMFAC model for on-road motor vehicle
estimates. In a letter dated November 15, 2019,
CARB withdrew the earlier submitted 2012 base
year emissions inventory for Ventura County in
light of the updated inventory in the 2016 Ventura
County AQMP. Letter dated November 15, 2019,
from Richard W. Corey, Executive Officer, CARB, to
Mike Stoker, Regional Administrator, EPA Region
IX. In section III.A of this document, we are
proposing approval of the superseding 2012 base
year emissions inventory in the 2016 Ventura
County AQMP.
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submittal dated December 5, 2018 and
discussed in more detail in the
following subsection. In addition, by
letter dated August 29, 2019, CARB has
provided some additional information
related to the motor vehicle emissions
budgets in the 2016 Ventura County
AQMP.22
2. CARB’s 2018 Updates to the
California State Implementation Plan
On December 5, 2018, CARB
submitted the 2018 Updates to the
California State Implementation Plan
(‘‘2018 SIP Update’’) to the EPA as a
revision to the California SIP.23 CARB
adopted the 2018 SIP Update on
October 25, 2018. CARB developed the
2018 SIP Update in response to the
court’s decision in South Coast II
vacating the 2008 Ozone SRR with
respect to the use of an alternate
baseline year for demonstrating RFP and
to provide additional information
pertaining to the contingency measure
requirement in the wake of the court
decision in Bahr v. EPA.24 The 2018 SIP
Update includes an RFP demonstration
using the required 2011 baseline year
for Ventura County for the 2008 ozone
NAAQS. The RFP demonstration in the
2018 SIP Update for Ventura County
supersedes and replaces the RFP
demonstration in the 2016 Ventura
County AQMP.25
The 2018 SIP Update includes
updates for 8 different California ozone
nonattainment areas. We have already
taken action to approve the San Joaquin
Valley and South Coast portions of the
2018 SIP Update.26 In today’s
document, we are proposing action on
22 Letter dated August 29, 2019, from Dr. Michael
T. Benjamin, Chief, Air Quality Planning and
Science Division, CARB, to Amy Zimpfer, Assistant
Director, Air Division, EPA Region IX, including
attachments A and B.
23 Letter dated December 5, 2018, from Richard
Corey, Executive Officer, CARB, to Mike Stoker,
Regional Administrator, EPA Region IX.
24 Bahr v. EPA, 836 F.3d 1218 (9th Cir. 2016)
(‘‘Bahr v. EPA’’). In Bahr v. EPA, the court rejected
the EPA’s longstanding interpretation of CAA
section 172(c)(9) as allowing for early
implementation of contingency measures. The court
concluded that a contingency measure must take
effect at the time the area fails to make RFP or attain
by the applicable attainment date, not before.
25 CARB withdrew the RFP demonstration from
the 2016 Ventura County AQMP in light of the
revised RFP demonstration for Ventura County in
the 2018 SIP Update. Letter dated November 15,
2019, from Richard W. Corey, Executive Officer,
CARB, to Mike Stoker, Regional Administrator, EPA
Region IX. In section III.E of this document, we are
proposing approval of the superseding RFP
demonstration for Ventura County in the 2018 SIP
Update.
26 84 FR 11198 (March 25, 2019) (final approval
of the San Joaquin Valley portion of the 2018 SIP
Update) and 84 FR 52005 (October 1, 2019) (final
approval of the South Coast portion of the 2018 SIP
Update).
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the Ventura County portion of the 2018
SIP Update. Also, to supplement the
contingency measure element of the
2016 Ventura County Ozone SIP, in a
letter dated August 30, 2019, CARB
forwarded to the EPA an August 16,
2019 letter of commitment from the
District.27 In its letter, the District
commits to modify at least one of three
existing rules to create a contingency
measure that will be triggered if the area
fails to meet an RFP milestone or to
attain the 2008 ozone NAAQS and to
transmit the rule, as amended, to CARB
for submittal to the EPA.28 In the August
30, 2019 letter, CARB commits to
submit the revised District rule or rules
to the EPA as a SIP revision within 12
months of the effective date of the EPA’s
final conditional approval of the
contingency measure element of the
2016 Ventura County Ozone SIP.
B. CAA Procedural Requirements for
Adoption and Submission of SIP
Revisions
Sections 110(a) and 110(l) of the CAA
require a state to provide reasonable
public notice and opportunity for public
hearing prior to the adoption and
submission of a SIP or SIP revision. To
meet this requirement, every SIP
submittal should include evidence that
adequate public notice was given and an
opportunity for a public hearing was
provided consistent with the EPA’s
implementing regulations in 40 CFR
51.102.
Both the District and CARB have
satisfied the applicable statutory and
regulatory requirements for reasonable
public notice and hearing prior to the
adoption and submittal of the SIP
revisions that comprise the 2016
Ventura County Ozone SIP. With
respect to the 2016 Ventura County
AQMP, the District provided two public
review periods: One for the initial draft
2016 Ventura County AQMP and a
second for the final draft 2016 Ventura
County AQMP. Combined, the public
review periods lasted 43 days. The
District published notices of the two
public review periods on its website and
in a local newspaper. The District also
published notice of a public hearing to
be held on February 14, 2017, for the
adoption of the 2016 Ventura County
AQMP. On February 14, 2017, the
District held the public hearing, and,
through a minute order, adopted the
2016 Ventura County AQMP and
27 Letter dated August 30, 2019, from Richard
Corey, Executive Officer, CARB, to Mike Stoker,
Regional Administrator, EPA Region IX.
28 Letter dated August 16, 2019, from Michael
Villegas, VCAPCD Air Pollution Control Officer, to
Richard Corey, CARB Executive Officer, provided
as enclosure to August 30, 2019 CARB letter.
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directed staff to forward the plan to
CARB for inclusion in the California
SIP.
CARB also provided public notice and
opportunity for public comment on the
2016 Ventura County AQMP. On
February 17, 2017, CARB released for
public review its Staff Report for the
2016 Ventura County AQMP and
published a notice of public meeting to
be held on March 23, 2017, to consider
adoption of the 2016 Ventura County
AQMP.29 On March 23, 2017, CARB
held the hearing and adopted the 2016
Ventura County AQMP as a revision to
the California SIP, and directed the
Executive Officer to submit the 2016
Ventura County AQMP to the EPA for
approval into the California SIP.30 On
April 11, 2017, the Executive Officer of
CARB submitted the 2016 Ventura
County AQMP to the EPA and included
a public comments log entry indicating
that there were no public comments
during the Board hearing held on March
23, 2017.31
With respect to the 2018 SIP Update,
CARB also provided public notice and
opportunity for public comment. On
September 21, 2018, CARB released for
public review the 2018 SIP Update and
published a notice of public meeting to
be held on October 23, 2018, to consider
adoption of the 2018 SIP Update.32 On
October 23, 2018, through Resolution
18–50, CARB adopted the 2018 SIP
Update. On December 5, 2018, CARB
submitted the 2018 SIP Update to the
EPA.
Based on information provided in
each of the SIP revisions summarized
above, the EPA has determined that all
hearings were properly noticed.
Therefore, we find that the submittals of
the 2016 Ventura County AQMP and the
2018 SIP Update meet the procedural
requirements for public notice and
hearing in CAA sections 110(a) and
110(l) and 40 CFR 51.102.
III. Evaluation of the 2016 Ventura
County Ozone SIP
A. Emissions Inventories
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1. Statutory and Regulatory
Requirements
CAA sections 172(c)(3) and 182(a)(1)
require states to submit for each ozone
29 Notice of Public Meeting to Consider the 2016
Ozone SIP for Ventura County, signed by Richard
Corey, Executive Officer, CARB, February 17, 2017.
30 CARB Resolution 17–5.
31 CARB ‘‘Public Comment Log,’’ dated March 30,
2017. See also, Transcript of the March 23, 2017
Meeting of the State of California Air Resources
Board, 7–8.
32 Notice of Public Meeting to Consider the 2018
Updates to the California State Implementation Plan
signed by Richard Corey, Executive Officer, CARB,
September 21, 2018.
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nonattainment area a ‘‘base year
inventory’’ that is a comprehensive,
accurate, current inventory of actual
emissions from all sources of the
relevant pollutant or pollutants in the
area. In addition, the 2008 Ozone SRR
requires that the inventory year be
selected consistent with the baseline
year for the RFP demonstration, which
is the most recent calendar year for
which a complete triennial inventory is
required to be submitted to the EPA
under the Air Emissions Reporting
Requirements.33
The EPA has issued guidance on the
development of base year and future
year emissions inventories for ozone
and other pollutants.34 Emissions
inventories for ozone must include
emissions of VOC and NOX and
represent emissions for a typical ozone
season weekday.35 States should
include documentation explaining how
the emissions data were calculated. In
estimating mobile source emissions,
states should use the latest emissions
models and planning assumptions
available at the time the SIP is
developed.36
Future baseline emissions inventories
must reflect the most recent population,
employment, travel and congestion
projections for the area. In this context,
future ‘‘baseline’’ emissions inventories
refer to emissions estimates for a given
year and area that reflect rules and
regulations and other measures that are
already adopted and that take into
account expected growth. Future
baseline emissions inventories are
necessary to show the projected
effectiveness of SIP control measures.
Both the base year and future year
inventories are necessary for
photochemical modeling to demonstrate
attainment.
2. Summary of State’s Submission
The 2016 Ventura County AQMP
includes base year (2012) and future
year baseline inventories for NOX and
VOC for the Ventura County ozone
nonattainment area. Documentation for
the inventories is found in Chapter 2
33 2008 Ozone SRR at 40 CFR 51.1115(a) and the
Air Emissions Reporting Requirements at 40 CFR
part 51, subpart A.
34 ‘‘Emissions Inventory Guidance for
Implementation of Ozone and Particulate Matter
National Ambient Air Quality Standards (NAAQS)
and Regional Haze Regulations,’’ EPA–454/B–17–
002, May 2017. At the time the 2016 Ventura
County AQMP was developed, the following EPA
emissions inventory guidance applied: ‘‘Emissions
Inventory Guidance for Implementation of Ozone
and Particulate Matter National Ambient Air
Quality Standards (NAAQS) and Regional Haze
Regulations,’’ EPA–454–R–05–001, August 2005.
35 40 CFR 51.1115(a) and (c), and 40 CFR
51.1100(bb) and (cc).
36 80 FR 12264, at 12290 (March 6, 2015).
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(‘‘2012 Baseline Emissions Inventory’’)
and Appendix A (‘‘Ventura County
Emissions Inventory Documentation’’)
of the 2016 Ventura County AQMP.
Because ozone levels in Ventura County
are typically higher from May through
October, these inventories represent
average summer day emissions. The
2012 base year and future year
inventories in the 2016 Ventura County
AQMP reflect District rules adopted
prior to July 2015, and CARB rules
adopted by November 2015.37 The
mobile source portions of both base year
and projected future year inventories
were developed using California’s EPAapproved mobile source emissions
model, EMFAC2014, for estimating onroad motor vehicle emissions.38
Emissions estimates of VOC and NOX
in the 2016 Ventura County AQMP are
grouped into two general categories: (1)
Stationary and area-wide sources, and
(2) mobile sources, which are comprised
of on-road motor vehicles and other
mobile (off-road) sources. Stationary
sources refer to larger ‘‘point’’ sources
that have a fixed geographic location,
such as power plants, industrial
engines, and oil storage tanks, and that
are subject to District permits. Areawide sources are emissions sources
occuring over a wide geographic area
such as consumer products and
architectural coatings. The emissions
inventories for the 2016 Ventura County
AQMP account for smaller permitted
stationary sources in the area source
categories. The mobile sources category
is divided into two major subcategories,
‘‘on-road’’ and ‘‘off-road’’ mobile
sources. On-road mobile sources
include light-duty automobiles, light-,
medium-, and heavy-duty trucks, and
motorcycles. Off-road mobile sources
include aircraft and boats.
For the 2016 Ventura County AQMP,
point source emissions for the 2012 base
year emissions inventory are based on
reported data from facilities using the
District’s annual emissions reporting
program, which applies under District
Rule 24 (‘‘Source Recordkeeping,
Reporting and Emissions Statements’’)
to all stationary sources in Ventura
County that emit more than 25 tons per
year (tpy) or more of VOC or NOX. Area
sources include smaller emissions
sources distributed across the
nonattainment area. CARB and the
37 The 2012 base year and future year baseline
emissions inventories in the 2016 Ventura County
AQMP exclude non-anthropogenic ‘‘natural
sources’’ emissions such as biogenics, geogenics,
and wildfires. However, emissions from such
natural sources are included in the emissions
inventories used for the attainment demonstration
because they affect ozone formation.
38 EMFAC is short for EMission FACtor.
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District estimate emissions for area
sources using established inventory
methods, including publicly available
emission factors and activity
information. Area source methodologies
are described in Appendix A of the 2016
Ventura County AQMP. To improve and
update the emissions inventory, District
staff evaluate the data and methods used
on an annual basis. CARB and District
staff coordinate the update process
through the State’s Emissions Inventory
Technical Advisory Committee.
On-road emissions inventories in the
2016 Ventura County AQMP are
calculated using CARB’s EMFAC2014
model 39 and the travel activity data
provided by the Southern California
Association of Governments (SCAG) in
‘‘The 2016–2040 Regional
Transportation Plan/Sustainable
Communities Strategy.’’ 40 CARB
provided emissions inventories for offroad equipment, including construction
and mining equipment, industrial and
commercial equipment, lawn and
garden equipment, agricultural
equipment, ocean-going vessels,
commercial harbor craft, locomotives,
cargo handling equipment, pleasure
craft, and recreational vehicles. CARB
uses several models to estimate
emissions for more than one hundred
off-road equipment categories.41 The
District estimates aircraft emissions
based on information provided by the
airport operators in Ventura County.
The 2016 Ventura County AQMP
distinguishes between emission sources
within Ventura County, which includes
coastal emissions (including marine
vessel emissions) within three miles of
the coastline, and emissions sources
operating outside the county but within
100 nautical miles of the coastline. The
latter are included in the Outer
Continental Shelf (OCS) category. The
base year emissions inventory reflects
only those emissions sources that
operate within the nonattainment area
(i.e., within the three miles of the
coastline), but OCS emissions sources
affect ozone concentrations in the
nonattainment area and thus are
included in the emissions inventories
used for the attainment demonstration
in the 2016 Ventura County AQMP.
Future emissions forecasts in the 2016
Ventura County AQMP are primarily
based on demographic and economic
growth projections provided by SCAG
(i.e., the metropolitan planning
organization (MPO) for Ventura
County), and control factors developed
by the District in reference to the 2012
base year. Growth factors used to project
these baseline inventories are derived
mainly from data obtained from
SCAG.42
Under EPA’s SIP regulations for
nonattainment new source review (NSR)
programs, a state may allow new major
stationary sources or major
modifications to use emission
reductions credits (ERCs) that were
generated through shutdown or
curtailed emissions units occuring
before the base year of an attainment
plan. However, to use such ERCs, the
projected emissions inventory used to
develop the attainment demonstration
must explicitly include the emissions
from such previously shutdown or
curtailed emissions units.43 The District
has elected to provide for use of prebase year ERCs as offsets by explicitly
including such ERCs in the 2020
attainment year inventory. The ERC setaside in the attainment year (2020)
amounts to 1.72 tons per day (tpd) of
VOC and 0.82 tpd of NOX.
Table 1 provides a summary of the
District’s 2012 base year and future
attainment year baseline emissions
estimates in tpd (average summer day)
for VOC and NOX. These inventories
provide the basis for the control
measure analysis and the attainment
demonstration in the 2016 Ventura
County AQMP. Based on the inventory
for 2012, stationary, area and mobile
sources contribute roughly equally to
county-wide VOC emissions, whereas
mobile sources are the predominant
sources of NOX emissions. The
inventory for 2012 also shows the extent
(about 40 percent) to which OCS
sources contribute to the overall
anthropogenic NOX emissions total used
for attainment modeling purposes.
TABLE 1—VENTURA COUNTY 2012 BASE YEAR AND 2020 ATTAINMENT YEAR EMISSIONS INVENTORIES
[Summer planning inventory, tpd]
2012
2020
Category
VOC
NOX
VOC
NOX
Stationary .........................................................................................................................................
Area Sources ...................................................................................................................................
On-Road Mobile Sources ................................................................................................................
Other (Off-Road) Mobile Sources ....................................................................................................
ERCs ................................................................................................................................................
8.55
11.57
8.54
8.14
................
2.08
0.95
12.62
8.78
................
8.67
10.91
4.21
6.63
1.72
1.87
0.62
6.01
7.25
0.82
Total for Ventura County Nonattainment Area .........................................................................
OCS Sources ...................................................................................................................................
36.81
0.96
24.44
16.11
32.14
1.37
16.57
15.49
Total Anthropogenic Emissions Used for Attainment Demonstration ......................................
37.76
40.55
33.50
32.06
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Source: 2016 Ventura County AQMP, Appendix A, tables A–7 and A–8. The sum of the emissions values may not equal the total shown due
to rounding of the numbers.
Following the South Coast II decision,
CARB submitted the 2018 SIP Update to
the EPA to, among other things, revise
the RFP demonstration in the 2016
Ventura County AQMP based on a 2011
RFP baseline year (i.e., rather than
2012).44 Our analysis of the emissions
inventories for the 2011 RFP baseline
year and RFP milestone years 2017 and
2020 can be found in section III.E
below.
39 In December 2015, the EPA approved
EMFAC2014 for SIP development and
transportation conformity purposes in California. 80
FR 77337 (December 14, 2015). EMFAC2014 was
the most recently approved version of the EMFAC
model that was available at the time of preparation
of the 2016 Ventura County AQMP. Recently, the
EPA approved an updated version of the EMFAC
model, EMFAC2017, for future SIP development
and transportation purposes in California. 84 FR
41717 (August 15, 2019).
40 See https://scagrtpscs.net/Pages/FINAL2016
RTPSCS.aspx.
41 2016 Ventura County AQMP, 22.
42 2016 Ventura County AQMP, Appendix A,
tables A–4 and A–6.
43 40 CFR 51.165(a)(3)(ii)(C)(1).
44 See 2018 SIP Update, Section III (‘‘SIP
Elements for Ventura County’’), 15–20; and
Appendix A, pp. A–7—A–10.
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3. The EPA’s Review of the State’s
Submission
We have reviewed the 2012 base year
emissions inventory in the 2016 Ventura
County AQMP and the inventory
methodologies used by the District and
CARB for consistency with CAA
requirements and EPA guidance. First,
as required by EPA regulation, we find
that the 2012 inventory includes
estimates for VOC and NOX for a typical
ozone season weekday, and that CARB
has provided adequate documentation
explaining how the emissions are
calculated. Second, we find that the
2012 base year emissions inventory in
the 2016 Ventura County AQMP reflects
appropriate emissions models and
methodologies, and, therefore,
represents a comprehensive, accurate,
and current inventory of actual
emissions during that year in the
Ventura County nonattainment area.
Third, we find that selection of year
2012 for the base year emissions
inventory is appropriate because it is
consistent with the 2011 RFP baseline
year (from the 2018 SIP Update) because
both inventories are derived from a
common set of models and methods.
Therefore, the EPA is proposing to
approve the 2012 emissions inventory
in the 2016 Ventura County AQMP as
meeting the requirements for a base year
inventory set forth in CAA section
182(a)(1) and 40 CFR 51.1115. In
addition, although the requirement for a
base year emissions inventory applies to
the nonattainment area, we find that the
District’s estimates of OCS emissions
out to 100 nautical miles (i.e., beyond
the nonattainment area boundary that
extends 3 miles offshore) are reasonable
and appropriate to include in the 2016
Ventura County AQMP given that such
emissions must be accounted for in the
ozone attainment demonstration for this
nonattainment area.
With respect to future year baseline
projections, we have reviewed the
growth and control factors and find
them acceptable and conclude that the
future baseline emissions projections in
the 2016 Ventura County AQMP reflect
appropriate calculation methods and the
latest planning assumptions.
Furthermore, we note that the future
year baseline projections take into
account emissions reductions from
adopted State and local rules and
regulations. As a general matter, the
EPA will approve a SIP revision that
takes emissions reduction credit for
such control measures only where the
EPA has approved the control measures
as part of the SIP. Table 1 in the EPA’s
memorandum dated September 11,
2019, to the docket for this rulemaking
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lists District VOC and NOX rules that
the 2016 Ventura County AQMP relied
upon in developing future year baseline
emissions projections. Table 1 also
includes information on EPA approval
of these rules and shows that emissions
reductions for stationary sources
assumed by the 2016 Ventura County
AQMP for future years are supported by
rules approved as part of the SIP.45 With
respect to mobile sources, the EPA has
taken action in recent years to approve
CARB mobile source regulations into
the California SIP.46 We therefore find
that the future year baseline projections
in the 2016 Ventura County AQMP are
properly supported by SIP-approved
stationary and mobile source control
measures.
B. Emissions Statement
1. Statutory and Regulatory
Requirements
Section 182(a)(3)(B)(i) of the Act
requires states to submit a SIP revision
requiring owners or operators of
stationary sources of VOC or NOX to
provide the state with statements of
actual emissions from such sources.
Statements must be submitted at least
every year and must contain a
certification that the information
contained in the statement is accurate to
the best knowledge of the individual
certifying the statement. Section
182(a)(3)(B)(ii) of the Act allows states
to waive the emissions statement
requirement for any class or category of
stationary sources that emit less than 25
tpy of VOC or NOX, if the state provides
an inventory of emissions from such
class or category of sources as part of the
base year or periodic inventories
required under CAA sections 182(a)(1)
and 182(a)(3)(A), based on the use of
emission factors established by the EPA
or other methods acceptable to the EPA.
The 2008 Ozone SRR provides that
nonattainment areas are subject to the
requirements of subpart 2 of part D of
title I of the CAA that apply for that
area’s classification.47 For all areas
classified under subpart 2, the
emissions statement requirement under
CAA section 182(a)(3)(B)(i) applies. The
preamble of the 2008 Ozone SRR states
that if an area has a previously approved
emissions statement rule for the 1997
ozone NAAQS or the 1-hour ozone
NAAQS that covers all portions of the
nonattainment area for the 2008 ozone
45 The list of rules in Table 1 of our September
11, 2019 memorandum includes all the District
rules for which specific future year emissions
reductions are assumed as shown in Table 3–1 of
the 2016 Ventura County AQMP.
46 See 81 FR 39424 (June 16, 2016), 82 FR 14446
(March 21, 2017), and 83 FR 23232 (May 18, 2018).
47 40 CFR 51.1102.
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NAAQS, such rule should be sufficient
for purposes of the emissions statement
requirement for the 2008 ozone
NAAQS.48 The state should review the
existing rule to ensure it is adequate
and, if so, may rely on it to meet the
emissions statement requirement for the
2008 ozone NAAQS. Where an existing
SIP-approved emissions statement rule
is adequate to meet the requirements of
the 2008 Ozone SRR, states can provide
the rationale for that determination to
the EPA in a written statement in their
SIP submittal for the 2008 ozone
NAAQS to meet this requirement. States
should identify the various
requirements and how each is met by
the existing SIP-approved emissions
statement program. Where an emissions
statement requirement is modified for
any reason, the state must provide the
revision to the emissions statement rule
as part of its SIP.
2. Summary of the State’s Submission
The 2016 Ventura County AQMP
addresses compliance with the
emissions statement requirement in
CAA section 182(a)(3)(B) for the 2008
ozone NAAQS by reference to District
Rule 24 (‘‘Source Recordkeeping,
Reporting and Emissions
Statements’’).49 District Rule 24
requires, among other things, emissions
reporting from all Ventura County
stationary sources of NOX and VOC, but
provides for waiver of the requirement
by the Air Pollution Control Officer for
sources that emit less than 25 tpy.50 The
EPA approved District Rule 24 as a
revision to the Ventura County portion
of the California SIP in 2000.51 The
District determined in the 2016 Ventura
County AQMP that the existing
provisions of District Rule 24 meet the
emissions statement requirements for
the 2008 ozone NAAQS.52
3. The EPA’s Review of the State’s
Submission
For this action, we have reviewed
VCAPCD’s evaluation of SIP-approved
District Rule 24 for compliance with the
specific requirements for emissions
statements under CAA section
182(a)(3)(B). We agree with the District
that District Rule 24 applies within the
entire ozone nonattainment area and
that the nonattainment area is the same
for both the 1-hour and 2008 ozone
NAAQS; applies to all stationary
sources of VOC and NOX, except those
48 See
80 FR 12264, at 12291 (March 6, 2015).
Ventura County AQMP, 16–18.
50 District Rule 24 refers to ‘‘reactive organic
compounds,’’ another term for ‘‘volatile organic
compounds.’’
51 65 FR 76567 (December 7, 2000).
52 2016 Ventura County AQMP, 17.
49 2016
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emitting less than 25 tpy for which the
District has waived the requirement
(consistent with CAA section
182(a)(3)(B)(ii)); and requires reporting,
on an annual basis, of total emissions of
VOC and NOX. Also, as required under
CAA section 182(a)(3)(B), we note that
District Rule 24 requires certification
that the information provided to the
District is accurate to the best
knowledge of the individual certifying
the emissions data.
Therefore, we propose to approve the
emissions statement element of the 2016
Ventura County AQMP as meeting the
requirements of CAA section
182(a)(3)(B) and the 40 CFR 51.1102.
C. Reasonably Available Control
Measures Demonstration
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1. Statutory and Regulatory
Requirements
CAA section 172(c)(1) requires that
each attainment plan provide for the
implementation of all RACM as
expeditiously as practicable (including
such reductions in emissions from
existing sources in the area as may be
obtained through implementation of
reasonably available control
technology), and also provide for
attainment of the NAAQS. The 2008
Ozone SRR requires that, for each
nonattainment area required to submit
an attainment demonstration, the state
concurrently submit a SIP revision
demonstrating that it has adopted all
RACM necessary to demonstrate
attainment as expeditiously as
practicable and to meet any RFP
requirements.53
The EPA has previously provided
guidance interpreting the RACM
requirement in the General Preamble for
the Implementation of the Clean Air Act
Amendments of 1990 (‘‘General
Preamble’’) and in a memorandum titled
‘‘Guidance on the Reasonably Available
Control Measure Requirement and
Attainment Demonstration Submissions
for Ozone Nonattainment Areas.’’ 54 In
short, to address the requirement to
adopt all RACM, states should consider
all potentially reasonable control
measures for source categories in the
nonattainment area to determine
whether they are reasonably available
for implementation in that area and
whether they would, if implemented
53 40
CFR 51.1112(c).
General Preamble, 57 FR 13498 at 13560
(April 16, 1992) and memorandum dated November
30, 1999, from John S. Seitz, Director, EPA Office
of Air Quality Planning and Standards (OAQPS), to
Regional Air Division Directors, titled ‘‘Guidance
on the Reasonably Available Control Measures
(RACM) Requirement and Attainment
Demonstration Submissions for Ozone
Nonattainment Areas.’’
54 See
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individually or collectively, advance the
area’s attainment date by one year or
more.55 Any measures that are
necessary to meet these requirements
that are not already either federally
promulgated, or part of the state’s SIP,
must be submitted in enforceable form
as part of the state’s attainment plan for
the area.56
2. Summary of the State’s Submission
For the 2016 Ventura County AQMP,
the District, the Ventura County
Transportation Commission (VCTC) and
CARB each undertook a process to
identify and evaluate potential RACM
that could contribute to expeditious
attainment of the 2008 ozone NAAQS in
Ventura County. We describe these
efforts in the three sections below. To
determine what RACM may be
necessary, the District compares, in the
2016 Ventura County AQMP, the
projected 2019 emissions inventory to
the 2020 attainment year. Comparing
the levels of VOC and NOX in these two
years, during which emissions are
declining, allows a simple subtraction to
determine what amount of emissions
reductions would result in 2020
attainment year-level emissions in the
year 2019. Since levels of VOC are
identical in both 2019 and 2020, no
reduction was necessary to achieve the
attainment year VOC emissions level.
However, for NOX the difference was 2
tpd, so the RACM analyses of the 2016
Ventura County AQMP appendices E, F
and G focus on determining whether
one or more control measures would be
potentially reasonable and would result
in a 2 tpd reduction of NOX emissions
prior to the 2020 attainment year.
55 Id. See also 44 FR 20372 (April 4, 1979), and
memorandum dated December 14, 2000, from John
S. Seitz, Director, EPA OAQPS, to Regional Air
Division Directors (Regions I, II, III, V and VI), titled
‘‘Additional Submission on RACM from States with
Severe 1-hour Ozone Nonattainment Area SIPs.’’
56 For ozone nonattainment areas classified as
Moderate or above, CAA section 182(b)(2) also
requires implementation of reasonably available
control technology (RACT) for all major sources of
VOC and for each VOC source category for which
the EPA has issued a control techniques guideline.
CAA section 182(f) requires that RACT under
section 182(b)(2) also apply to major stationary
sources of NOX. In Serious areas, a major source is
a stationary source that emits or has the potential
to emit at least 50 tpy of VOC or NOX (see CAA
section 182(c) and (f)). Under the 2008 Ozone SRR,
states were required to submit SIP revisions
meeting the RACT requirements of CAA sections
182(b)(2) and 182(f) no later than 24 months after
the effective date of designation for the 2008 Ozone
NAAQS and to implement the required RACT
measures as expeditiously as practicable but no
later than January 1 of the 5th year after the
effective date of designation (see 40 CFR
51.1112(a)). California submitted the CAA section
182 RACT SIP for Ventura County on July 18, 2014,
and the EPA fully approved this submission at 80
FR 2016 (January 15, 2015).
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a. District’s RACM Analysis
The District’s portion of the RACM
demonstration for the 2008 ozone
NAAQS focuses on stationary source
controls and is described in the 2016
Ventura County AQMP on pages 54 and
55, and in Appendix E (‘‘Ventura
County Stationary Source Reasonably
Available Control Measure
Assessment’’). Appendix E contains
analyses of all potential stationary
source control measures in the District’s
jurisdiction.
As background, the District notes that
Ventura County was nonattainment for
all prior ozone NAAQS, therefore the
District’s RACM analysis builds upon a
foundation of District rules developed
for earlier ozone plans. We provide a list
of the District’s NOX and VOC rules
approved into the California SIP in
Table 1 of our September 11, 2019
memorandum to the docket for this
proposed action.57 The 48 SIP-approved
District VOC or NOX rules listed in
Table 1 of our September 11, 2019
memorandum establish emission limits
or other types of emissions controls for
a wide range of sources, including use
of solvents, refineries, gasoline storage,
architectural coatings, oilfield drilling
operations, various types of commercial
coatings, boilers, steam generators and
process heaters, marine coating
operations, dry cleaning, and others.
These rules have already provided
significant and ongoing reductions
toward attainment of the 2008 ozone
NAAQS by 2020. In describing its
stationary source controls, the District
also notes the EPA’s 2015 approval of its
reasonably available control technology
(RACT) SIP and our finding in that
action that District rules that apply to
ozone precursor emissions fulfill RACT
requirements for the 2008 ozone
NAAQS.58
For the stationary source RACM
demonstration, the District evaluated
the VOC and NOX rules that were not
fully addressed in the District’s 2014
RACT SIP for potential RACM
emissions reductions. The District
compared that subset of District rules to
analogous rules adopted by other air
districts having nonattainment areas
with higher ozone nonattainment
classifications (i.e., South Coast and San
Joaquin Valley, which are both
‘‘Extreme’’ nonattainment areas for the
57 Memorandum dated September 11, 2019, from
John J. Kelly, Air Planning Office, EPA Region 9 to
‘‘Approval of Air Quality Implementation Plans;
California; Ventura County; 8-Hour Ozone
Nonattainment Area Requirements; Docket ID EPA–
R09–OAR–2018–0146,’’ subject: District Rules
Assumed for Purposes of Developing Baseline
Emissions Projections.
58 80 FR 2016, January 15, 2015.
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2008 ozone NAAQS), as well as certain
other air districts such as the Bay Area
Air Quality Management District, to
evaluate whether control technologies
available and cost-effective within other
areas would be available and costeffective for use in Ventura County. The
District also identified a few rules from
other air districts that apply to
unregulated source categories in
Ventura County. Tables E–2 and E–3 in
Appendix E of the 2016 Ventura County
AQMP list the rules that the District
evaluated for the RACM demonstration.
Table E–2 includes 13 rules that the
District has previously adopted that
were compared to rules in other areas.
Table E–3 includes five source
categories the District evaluated, where
there is no corresponding rule for that
source category in Ventura County.
The District provides an evaluation of
the controls it reviewed for RACM
purposes in Appendix E of the 2016
Ventura County AQMP. The evaluation
includes the following: Description of
the Ventura County sources within the
category or sources that would be
subject to the rule; potential NOX and
VOC emissions reductions expected
from implementing the rule in Ventura
County for the source category affected
by the rule; discussion of the current
requirements of the rule; and discussion
of potential additional control measures.
This includes comparison of each
District rule to analogous control
measures adopted by other agencies.
Among the 13 existing District NOX or
VOC rules that the District compared to
rules in other areas, the District found
that eight of the VCAPCD rule emission
limits were as stringent as those found
in analogous rules adopted by the other
districts or were not applicable for the
purposes of comparison. The District
estimated the emissions reductions for
the remaining five rules that could be
made more stringent to match the most
stringent of the other district rules’
limits.59 Among the five source
categories for which the District has no
current rules, the District identified four
categories for which other districts have
adopted rules that could be adopted for
Ventura County.60
The District estimated the potential
emissions reduction associated with
revisions to the five existing District
59 The five District rules include Rule 74.2
(‘‘Architectural Coatings’’), Rule 74.19.1 (‘‘Screen
Printing Operations’’), Rule 74.21 (‘‘Semiconductor
Manufacturing’’); Rule 74.22 (‘‘Natural Gas-Fired,
Central Fan-Type Furnaces’’), and Rule 74.34
(‘‘NOX Reductions from Miscellaneous Sources’’).
60 The four source categories include composting
and organic material conversion operations,
vacuum truck operations, emissions of oxides of
nitrogen from commercial food ovens, and food
products manufacturing and processing operations.
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rules and adoption of the four new rules
to be approximately 0.5 tpd of VOC and
0.01 tpd of NOX. Based on the District’s
threshold of 2 tpd of NOX as the
minimum reduction necessary to
advance attainment by one year, the
District concluded that its current set of
VOC and NOX rules represent all RACM
within regulatory jurisdiction, and that
no further RACM are necessary to meet
the RACM requirement for the 2008
ozone NAAQS. We note that the new
stationary source control measures in
the 2016 Ventura County AQMP include
revisions to two existing District rules,
Rule 74.2 (‘‘Architectural Coatings’’)
and Rule 74.22 (‘‘Natural Gas-Fired,
Central Fan-Type Furnaces’’), and
adoption of one new rule, proposed new
Rule 74.32 (‘‘Compostable Material
Handing and Conversion Operations’’),
that are part of the RACM analysis.
However, the purpose of these
stationary source control measures in
the 2016 Ventura County AQMP was
not to meet the RACM requirement but
to provide emissions reductions for the
2015 ozone NAAQS and to fulfill State
air quality requirements.
b. Local Jurisdiction’s RACM Analysis
and Transportation Control Measures
Transportation Control Measures
(TCMs) are projects that reduce air
pollutants from transportation sources
by reducing vehicle use, traffic
congestion, or vehicle miles traveled.
Appendix B (‘‘Ventura County
Transportation Control Measure
Commitments’’) of the 2016 Ventura
County AQMP lists the current TCMs
identified by SCAG and the District as
committed TCMs. ‘‘Committed’’ TCMs
are subject to the timely implementation
requirement in CAA section
176(c)(2)(B). For the 2016 Ventura
County AQMP, the District and VCTC
worked together to determine whether
additional TCMs are necessary to meet
the RACM requirement. The TCM
RACM component of the 2016 Ventura
County AQMP is found on page 55 of
the AQMP and in Appendix F (‘‘Ventura
County Transportation Control
Measures Reasonably Available Control
Measure Assessment’’).
First, the District prepared a list of
candidate RACM using the CAA’s list of
TCMs in section 108(f)(1)(A) by
reviewing the TCMs in the 2008 Ventura
County AQMP, and other air district
and planning agency plans, such as the
2012 South Coast AQMP, 2007 San
Joaquin Valley Ozone Plan, 2013
Sacramento Regional 8-Hour Ozone
Attainment and Reasonable Further
Progress Plan, and the 2004/2007
Metropolitan Washington Council of
Governments SIP. Second, the District,
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along with staff of the VCTC, sorted the
candidate TCMs based on their
feasibility or infeasibility for
implementation in Ventura County.61
Table F–1 of Appendix F of the 2016
Ventura County AQMP summarizes the
results of the sorting process.
Justification is provided in Table F–1 for
those candidate TCMs deemed by the
District and VCTC to be infeasible. All
candidate TCMs are organized in Table
F–1 according to the sixteen categories
specified in section 108(f)(1)(A) of the
CAA.
The District found that the majority of
TCMs that were deemed to be feasible
in Ventura County were already being
implemented, or had been implemented
in the county, and that implementing all
additional feasible TCMs in the county
would not advance attainment by a year.
Based on its comprehensive review of
TCM projects in other nonattainment
areas or otherwise identified, the
District determined that the TCMs being
implemented in Ventura County are
inclusive of all RACM.62
c. CARB’s RACM Analysis
Source categories for which CARB has
primary jurisdiction for reducing
emissions in California include most
new and existing on- and off-road
engines and vehicles, motor vehicle
fuels, and consumer products. CARB’s
RACM assessment is contained in the
2016 Ventura County AQMP, Appendix
G (‘‘Ventura County Mobile Source
Reasonably Available Control Measures
Assessment’’). In the 2016 Ventura
County AQMP, CARB has also provided
a general description of CARB’s key
mobile source regulations and programs
and a comprehensive table listing onand off-road mobile source regulatory
actions taken by CARB from 1985
through 2016.63 The RACM assessment
contains CARB’s evaluation of mobile
source and other statewide control
measures that reduce emissions of NOX
and VOC in Ventura County.
Given the need for substantial
emissions reductions from mobile and
area sources to meet the NAAQS in
California nonattainment areas, CARB
established stringent control measures
for on-road and off-road mobile sources
and the fuels that power them.
California has unique authority under
CAA section 209 (subject to a waiver by
the EPA) to adopt and implement new
61 See 2016 Ventura County AQMP, Appendix F,
page F–1.
62 See 2016 Ventura County AQMP, Appendix F,
page F–3.
63 See 2016 Ventura County AQMP, Appendix C
(‘‘Key ARB Mobile Source Regulations and
Programs’’) and Appendix D (‘‘Air Resources Board
Control Measures, 1985–2016’’).
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emission standards for many categories
of on-road vehicles and engines, and
new and in-use off-road vehicles and
engines.
CARB’s mobile source program
extends beyond regulations that are
subject to the waiver or authorization
process set forth in CAA section 209, to
include standards and other
requirements to control emissions from
in-use heavy-duty trucks and buses,
gasoline and diesel fuel specifications,
and many other types of mobile sources.
Generally, these regulations have been
submitted and approved as revisions to
the California SIP.64
In the RACM assessment, CARB
concludes that there are no additional
RACM that would advance attainment
of the 2008 ozone NAAQS in Ventura
County. As a result, CARB concludes
that California’s mobile source programs
fully meet the RACM requirement.65
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3. The EPA’s Review of the State’s
Submission
As described above, the District
already implements many rules to
reduce VOC and NOX emissions from
stationary sources in Ventura County.
For the 2016 Ventura County AQMP,
the District evaluated a range of
potentially available control measures.
We find that the process followed by the
District in the 2016 Ventura County
AQMP to identify additional RACM is
generally consistent with the EPA’s
recommendations in the General
Preamble, the District’s evaluation of
potential measures is appropriate, and
the District has provided reasoned
justifications for rejection of measures
deemed not reasonably available.
With respect to mobile sources,
CARB’s current program addresses the
full range of mobile sources in Ventura
County through regulatory programs for
both new and in-use vehicles. With
respect to TCMs, we find that the
District’s and VCTC’s process for
identifying additional TCM RACM and
the District’s conclusion that the TCMs
being implemented in Ventura County
(i.e., the TCMs listed in Table B–1 in
Appendix B of the 2016 Ventura County
AQMP) are inclusive of all TCM RACM
to be reasonably justified and
supported.
Based on our review of these RACM
analyses, the District’s and CARB’s
64 See, e.g., the EPA’s approval of standards and
other requirements to control emissions from in-use
heavy-duty diesel-powered trucks, at 77 FR 20308
(April 4, 2012), revisions to the California on-road
reformulated gasoline and diesel fuel regulations at
75 FR 26653 (May 12, 2010), and revisions to the
California motor vehicle inspection and
maintenance program at 75 FR 38023 (July 1, 2010).
65 See 2016 Ventura County AQMP, Appendix G,
page G–5.
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adopted rules, and SCAG’s committed
TCMs, we propose to find that there are,
at this time, no additional RACM that
would advance attainment of the 2008
ozone NAAQS in Ventura County.66 For
the foregoing reasons, we propose to
find that the 2016 Ventura County
AQMP provides for the implementation
of all RACM as required by CAA section
172(c)(1) and 40 CFR 51.1112(c).
D. Attainment Demonstration
1. Statutory and Regulatory
Requirements
An attainment demonstration consists
of the following: (1) Technical analyses,
such as base year and future year
modeling, to locate and identify sources
of emissions that are contributing to
violations of the ozone NAAQS within
the nonattainment area (i.e., analyses
related to the emissions inventory for
the nonattainment area and the
emissions reductions necessary to attain
the standard); (2) a list of adopted
measures (including RACT controls)
with schedules for implementation and
other means and techniques necessary
and appropriate for demonstrating RFP
and attainment as expeditiously as
practicable but no later than the outside
attainment date for the area’s
classification; (3) a RACM analysis; and
(4) contingency measures required
under sections 172(c)(9) and 182(c)(9) of
the CAA that can be implemented
without further action by the state or the
EPA to cover emissions shortfalls in
RFP plans and failures to attain.67 This
subsection of today’s proposed rule
addresses the first two components of
the attainment demonstration—the
technical analyses and a list of adopted
measures. Section III.C, Reasonably
Available Control Measures
Demonstration, of this document
addresses the RACM component, and
section III.F, Contingency Measures,
addresses the contingency measures
component of the attainment
demonstration in the 2016 Ventura
County AQMP.
With respect to the technical analyses,
section 182(c)(2)(A) of the CAA requires
that a plan for an ozone nonattainment
area classified Serious or above include
a ‘‘demonstration that the plan . . . will
provide for attainment of the ozone
[NAAQS] by the applicable attainment
date. This attainment demonstration
must be based on photochemical grid
modeling or any other analytical
method determined . . . to be at least as
effective.’’ The attainment
demonstration predicts future ambient
concentrations for comparison to the
NAAQS, making use of available
information on measured
concentrations, meteorology, and
current and projected emissions
inventories of ozone precursors,
including the effect of control measures
in the plan.
Areas classified Serious for the 2008
ozone NAAQS must demonstrate
attainment as expeditiously as
practicable, but no later than 9 years
after the effective date of designation to
nonattainment. Ventura County was
designated nonattainment effective July
20, 2012, and the area must demonstrate
attainment of the 2008 ozone NAAQS
by July 20, 2021.68 An attainment
demonstration must show attainment of
the standards for a full calendar year
before the attainment date, so in
practice, Serious nonattainment areas
must demonstrate attainment in 2020.
The EPA’s recommended procedures
for modeling ozone as part of an
attainment demonstration are contained
in ‘‘Modeling Guidance for
Demonstrating Attainment of Air
Quality Goals for Ozone, PM2.5, and
Regional Haze’’ (‘‘Modeling
Guidance’’).69 The Modeling Guidance
includes recommendations for a
modeling protocol, model input
preparation, model performance
evaluation, use of model output for the
numerical NAAQS attainment test, and
modeling documentation. Air quality
modeling is performed using
meteorology and emissions from a base
year, and the predicted concentrations
from this base case modeling are
compared to air quality monitoring data
from that year to evaluate model
performance.
Once the model performance is
determined to be acceptable, future year
68 80
66 We
find that the District’s identification of a 2tpd threshold for the minimum reduction necessary
to advance attainment of the 2008 ozone NAAQS
in Ventura County by one year to be reasonable.
The nonattainment area relies on both VOC and
NOX controls, and the potential emissions
reductions of NOX and VOC (considered together)
from potential RACM (stationary source, TCM, and
mobile) would not achieve the necessary emissions
reductions to advance attainment by one year, and
therefore, such additional measures are not required
to meet the RACM requirement.
67 78 FR 34178, at 34184 (June 6, 2013) (proposed
rule for implementing the 2008 ozone NAAQS).
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FR 12264, at 12268 (March 6, 2015).
Guidance, December 2014 Draft, EPA
OAQPS; available at https://www.epa.gov/scram/
state-implementation-plan-sip-attainmentdemonstration-guidance. The 2014 modeling
guidance updates, but is largely consistent with, the
earlier ‘‘Guidance on the Use of Models and Other
Analyses for Demonstrating Attainment of Air
Quality Goals for the 8-Hour Ozone and PM2.5
NAAQS and Regional Haze,’’ EPA–454/B–07–002,
April 2007. Additional EPA modeling guidance can
be found in 40 CFR 51 Appendix W, ‘‘Guideline on
Air Quality Models,’’ 82 FR 5182 (January 17,
2017); available at https://www.epa.gov/scram/
clean-air-act-permit-modeling-guidance.
69 Modeling
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emissions are simulated with the model.
The relative (or percent) change in
modeled concentration due to future
emissions reductions provides a
Relative Response Factor (RRF). Each
monitoring site’s RRF is applied to its
monitored base year design value to
provide the future design value for
comparison to the NAAQS. The
Modeling Guidance also recommends
supplemental air quality analyses,
which may be used as part of a Weight
of Evidence (WOE) analysis. A WOE
analysis corroborates the attainment
demonstration by considering evidence
other than the main air quality modeling
attainment test, such as trends and
additional monitoring and modeling
analyses.
The Modeling Guidance does not
require a particular year to be used as
the base year for 2008 ozone NAAQS
plans.70 The Modeling Guidance states
that the most recent year of the National
Emissions Inventory may be appropriate
for use as the base year for modeling,
but that other years may be more
appropriate when considering
meteorology, transport patterns,
exceptional events, or other factors that
may vary from year to year.71 Therefore,
the base year used for the attainment
demonstration need not be the same
year used to meet the requirements for
RFP.
With respect to the list of adopted
measures, CAA section 172(c)(6)
requires that nonattainment area plans
include enforceable emissions
limitations, and such other control
measures, means or techniques
(including economic incentives such as
fees, marketable permits, and auctions
of emission rights), as well as schedules
and timetables for compliance, as may
be necessary or appropriate to provide
for timely attainment of the NAAQS.72
Under the 2008 Ozone SRR, all control
measures needed for attainment must be
implemented no later than the
beginning of the attainment year ozone
season.73 The attainment year ozone
season is defined as the ozone season
immediately preceding a nonattainment
area’s maximum attainment date.74
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2. Summary of the State’s Submission
a. Photochemical Modeling
The 2016 Ventura County AQMP
includes photochemical modeling for
the 2008 ozone NAAQS. The South
Coast Air Quality Management District
(SCAQMD) performed the air quality
70 Modeling
Guidance at section 2.7.1.
71 Ibid.
72 See
also CAA section 110(a)(2)(A).
CFR 51.1108(d).
74 40 CFR 51.1100(h).
73 40
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modeling for the 2016 Ventura County
AQMP. The modeling relies on a 2012
base year and demonstrates attainment
of the 2008 ozone NAAQS by the
applicable Serious area attainment year
(i.e. 2020).
The modeling and modeled
attainment demonstration are described
in Chapter 5 (‘‘Attainment
Demonstration’’) of the 2016 Ventura
County AQMP and in four appendices.
Appendix H (‘‘Protocol for
Photochemical Modeling of Ozone in
Ventura County’’) of the 2016 Ventura
County AQMP is the modeling protocol
and contains all the elements
recommended in the Modeling
Guidance. Those include: Selection of
model, time period to model, modeling
domain, and model boundary
conditions and initialization
procedures; a discussion of emissions
inventory development and other model
input preparation procedures; model
performance evaluation procedures;
selection of days; and other details for
calculating RRFs. Appendix H of the
2016 Ventura County AQMP also
provides the coordinates of the
modeling domain and thoroughly
describes the development of the
modeling emissions inventory,
including its chemical speciation, its
spatial and temporal allocation, its
temperature dependence, and quality
assurance procedures.
The modeling analysis used version
5.0.2 of the Community Multiscale Air
Quality (CMAQ) photochemical model,
developed by the EPA. To prepare
meteorological input for CMAQ, the
Weather and Research Forecasting
model version 3.6 (WRF) from the
National Center for Atmospheric
Research was used. CMAQ and WRF are
both recognized in the Modeling
Guidance as technically sound, state-ofthe-art models. The areal extent and the
horizontal and vertical resolution used
in these models were adequate for
modeling ozone in the southern
California domain, including Ventura.
The performance of the WRF
meteorological model was assessed
through a series of simulations, and the
SCAQMD concluded that the daily WRF
simulation for 2012 provided
representative meteorological fields that
well characterized the observed
conditions. The SCAQMD’s conclusions
were supported by hourly time series
graphs of wind speed, direction, and
temperature.75
75 SCAQMD, 2016 South Coast AQMP (March
2017), Appendix V (‘‘Modeling and Attainment
Demonstration’’), Chapter 3 (‘‘Meteorological
Modeling and Sensitivity Analyses’’), Attachment 1
(‘‘WRF Model Performance Time Series’’).
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Ozone model performance statistics
are described in the 2016 Ventura
County AQMP Appendix I (‘‘Ventura
County Community Multiscale Air
Quality Model Performance Analysis’’),
which include tables of statistics
recommended in the Modeling
Guidance for 8-hour daily maximum
ozone for Ventura County. Hourly time
series are presented, as well as density
scatter plots and plots of bias against
concentration. Note that only relative
changes are used from the modeling,
therefore the overprediction or
underprediction of absolute ozone
concentrations does not mean that
future concentrations will be
overestimated or underestimated.
After model performance for the 2012
base case was accepted, the model was
applied to develop RRFs for the
attainment demonstration. This entailed
running the model with the same
meteorological inputs as before, but
with adjusted emissions inventories to
reflect the expected changes between
2012 and the 2020 attainment year. The
base year or ‘‘reference year’’ modeling
inventory was the same as the inventory
for the modeling base case. The 2020
inventory projects the base year into the
future by including the effect of
economic growth and emissions control
measures. The set of 153 days from May
1 through September 30, 2012, was
simulated and analyzed to determine
daily 8-hour average maximum ozone
concentrations for the 2020 emissions
inventory. To develop the RRFs for the
2008 ozone NAAQS, only the top 10
days were used.
The Modeling Guidance addresses
attainment demonstrations with ozone
NAAQS based on 8-hour averages. For
the 2008 ozone NAAQS, the 2016
Ventura County AQMP carried out the
attainment test procedure consistent
with the Modeling Guidance. The RRFs
were calculated as the ratio of future to
base year concentrations. The resulting
RRFs were then applied to 2012
weighted base year design values 76 for
each monitor to arrive at a 2020 future
year design value.77 The highest 2020
ozone design value is 0.072 ppm at the
Simi Valley site; this value
demonstrates attainment of the
76 The Modeling Guidance recommends that
RRFs be applied to the average of three three-year
design values centered on the base year, in this case
the design values for 2010–2012, 2011–2013, and
2012–2014. This amounts to a 5-year weighted
average of individual year 4th-high concentrations,
centered on the base year of 2012, and so is referred
to as a weighted design value.
77 2016 Ventura County AQMP, Appendix I,
Table I–2 (‘‘Base Year and Future Year Ozone
Design Values’’).
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corresponding 2008 ozone NAAQS of
0.075 ppm.
The 2016 Ventura County AQMP
modeling also includes a WOE
demonstration in Appendix K (Ventura
County Weight of Evidence Assessment)
prepared by CARB. To complement
regional photochemical modeling
analyses included in the 2016 Ventura
County AQMP, the WOE demonstration
includes detailed analyses of ambient
ozone data, county level precursor
emissions trends, population exposure
trends, and a discussion of conditions
that contribute to exceedances of the
0.075 ppm 2008 ozone NAAQS. Further,
the rate of progress toward air quality
goals was evaluated by considering
trends in ozone design values, precursor
emissions reductions, and the
relationship between ozone air quality
and past emissions reductions.78
Finally, the 2016 Ventura County
AQMP includes an unmonitored area
analysis for the 2008 ozone NAAQS to
assess the attainment status of locations
other than monitoring sites.79 The
Modeling Guidance describes a
‘‘gradient adjusted spatial fields’’
procedure along with the EPA software
(i.e., Modeled Attainment Test
Software) used to carry it out.80 The
unmonitored area analysis in the 2016
Ventura County AQMP shows
concentrations below the 2008 ozone
NAAQS for all locations.81
b. Control Strategy for Attainment
The control strategy for attainment of
the 2008 ozone NAAQS in the 2016
Ventura County AQMP relies on
emissions reductions from baseline (i.e.,
already-adopted) measures. The
baseline control measures include the
District’s stationary source rules,
including those specifically included in
the emissions inventories prepared for
the 2016 Ventura County AQMP,82 and
CARB’s mobile source and consumer
product rules adopted through 2016 as
listed in Appendix D of the 2016
Ventura County AQMP.
c. Attainment Demonstration
Table 2 below summarizes the
attainment demonstration for the 2008
ozone NAAQS by listing the base year
(2012) emissions level, the modeled
attainment emissions level, and the
reductions that the District and CARB
estimate to achieve through baseline
control measures taking into account
growth and the District’s ERC balance.
As shown in Table 2, baseline measures
are expected to reduce base year (2012)
emissions of NOX by 21 percent and
VOC emissions by 11 percent by the
2020 attainment year, notwithstanding
growth and the ERC balance, and to
attain the 2008 ozone NAAQS in
Ventura County by that year.
TABLE 2—SUMMARY OF VENTURA COUNTY 2008 OZONE NAAQS ATTAINMENT DEMONSTRATION
[Summer planning inventory, tpd]
A 2012 Base Year Emissions Level a ..............................................................................................................................................
B—2020 Modeled Attainment Emissions Level a ..............................................................................................................................
C Total Reductions Needed from 2012 Base Year Levels to Demonstrate Attainment (A–B) ......................................................
D Reductions from Baseline (i.e., adopted) Measures, net of growth and ERC balance ..............................................................
E 2020 Emissions with Reductions from Baseline Control Strategy (compare to Row B) ............................................................
Attainment demonstrated? ..........................................................................................................................................................
NOX
VOC
40.55
32.06
8.49
8.49
32.06
Yes
37.76.
33.50.
4.26.
4.26.
33.50.
Yes.
Notes and sources:
a 2016 Ventura County AQMP, Appendix A, tables A–6 and A–7. Includes emissions out to 100 nautical miles from the coast. Year 2020 Modeled Attainment Emissions Level includes ERC balance.
3. The EPA’s Review of the State’s
Submission
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a. Photochemical Modeling
To approve a SIP’s attainment
demonstration, the EPA must make
several findings. First, we must find that
the demonstration’s technical bases,
including the emissions inventories and
air quality modeling, are adequate. As
discussed above in section III.A of this
document, we are proposing to approve
the base year emissions inventory and to
find that the future year emissions
projections in the 2016 Ventura County
AQMP reflect appropriate calculation
methods and that the latest planning
assumptions are properly supported by
SIP-approved stationary and mobile
source measures. These are the same
inventories used for the attainment
demonstration, and thus, we find that
78 2016 Ventura County AQMP, Appendix K,
page K–2.
79 2016 Ventura County AQMP, Appendix J
(‘‘Ventura County Unmonitored Area Analysis’’),
prepared by the SCAQMD.
80 Modeling Guidance, section 4.7.
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the emissions portion of the attainment
demonstration is adequate.
With respect to the photochemical
modeling in the 2016 Ventura County
AQMP, based on our review of the 2016
Ventura County AQMP, the EPA finds
that the modeling is adequate for
purposes of supporting the attainment
demonstration. First, we note the
extensive discussion of modeling
procedures, tests, and performance
analyses called for in the Modeling
Protocol (i.e., Appendix H) and the good
model performance. Second, we find the
WRF meteorological model results and
performance statistics, including hourly
time series graphs of wind speed,
direction, and temperature for the
southern California modeling domain,
to be satisfactory and consistent with
our Modeling Guidance.83
81 2016 Ventura County AQMP, Appendix J,
Figure J–3 (‘‘2020 Predicted 8-hr Ozone Design
Values’’).
82 See 2016 Ventura County AQMP, Appendix A,
Table A–5 (‘‘District Rules Included in the SIP
Inventory’’).
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The model performance statistics for
ozone are described in the 2016 Ventura
County AQMP, Appendix I. The
analysis evaluated how well the
photochemical model for the 2016
Ventura County AQMP was able to
predict 8-hour ozone concentrations at
each monitoring site in the county
compared to observed 8-hour ozone
concentrations at those same monitoring
sites and is based on the statistical
evaluation recommended in the
Modeling Guidance. The base year
average regional model performance
was evaluated for May through
September 2012 for days when
maximum 8-hour ozone levels were at
least 60 ppb.84 Ozone measurements
from air quality monitors in Thousand
Oaks, Piru, Ojai, Simi Valley, and El Rio
were compiled for the analysis. To
develop the RRFs for the 2008 ozone
83 Modeling
Guidance, 30.
stations with more than 74.5% (the EPA’s
data completeness requirement) of the hourly
measurements during each month of the ozone
season were included in the analysis.
84 Only
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NAAQS, only the top 10 days were
used. This is consistent with EPA
guidance, which recommends the use of
only the top 10 days in the RRF
calculation because the modeling
capability to predict high concentrations
is more important than the prediction of
low concentrations.85
The 2016 Ventura County AQMP’s
unmonitored area analysis showed
concentrations below the 2008 ozone
NAAQS for all locations. This analysis
adds assurance to the attainment
demonstration that all locations in
Ventura County will attain the 2008
ozone NAAQS by the 2020 attainment
year. In addition, the WOE analyses
presented in the 2016 Ventura County
AQMP provide additional information
with respect to the sensitivity to
emission changes and improve the
understanding of the model
performance. We are proposing to find
the air quality modeling in the 2016
Ventura County AQMP adequate to
support the attainment demonstration
for the 2008 ozone NAAQS in Ventura
County, based on reasonable
meteorological and ozone modeling
performance, and further supported by
the unmonitored area and WOE
analyses.
b. Control Strategy for Attainment
Second, we must find that the
emissions reductions that are relied on
for attainment are creditable and are
sufficient to provide for attainment. As
shown in Table 2 above, the 2016
Ventura County AQMP relies on
baseline measures to achieve all the
emissions reductions needed to attain
the 2008 ozone NAAQS by 2020. The
baseline measures are approved into the
SIP and, as such, are fully creditable.
c. Attainment Demonstration
Based on our proposed
determinations that the photochemical
modeling and control strategy are
acceptable, we propose to approve the
attainment demonstration for the 2008
ozone NAAQS in the 2016 Ventura
County AQMP as meeting the
requirements of CAA section
182(c)(2)(A) and 40 CFR 51.1108.
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E. Rate of Progress Plan and Reasonable
Further Progress Demonstration
1. Statutory and Regulatory
Requirements
Requirements for RFP for ozone
nonattainment areas are specified in
CAA sections 172(c)(2), 182(b)(1), and
182(c)(2)(B). Under CAA section 171(1),
RFP is defined as meaning such annual
incremental reductions in emissions of
85 Modeling
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the relevant air pollutant as are required
under CAA part D (‘‘Plan Requirements
for Nonattainment Areas’’) or may
reasonably be required by the EPA for
the purpose of ensuring attainment of
the applicable NAAQS by the applicable
date. CAA section 172(c)(2) generally
requires that a nonattainment plan
include provisions for RFP. CAA section
182(b)(1) specifically requires that
ozone nonattainment areas that are
classified as Moderate or above
demonstrate a 15 percent reduction in
VOC between the years of 1990 and
1996. The EPA has typically referred to
section 182(b)(1) as the rate of progress
(ROP) requirement. For ozone
nonattainment areas classified as
Serious or higher, section 182(c)(2)(B)
requires reductions averaged over each
consecutive 3-year period, beginning 6
years after the baseline year until the
attainment date, of at least 3 percent of
baseline emissions per year. The
provisions in CAA section
182(c)(2)(B)(ii) allow an amount less
than 3 percent of such baseline
emissions each year if the state
demonstrates to the EPA that the plan
includes all measures that can feasibly
be implemented in the area in light of
technological achievability.
In the 2008 Ozone SRR, the EPA
provides that areas classified Moderate
or higher for the 2008 ozone NAAQS
will have met the ROP requirements of
CAA section 182(b)(1) if the area has a
fully approved 15 percent ROP plan for
the 1-hour or 1997 ozone NAAQS,
provided that the boundaries of the
ozone nonattainment areas are the
same.86 For such areas, the EPA
interprets the RFP requirements of CAA
section 172(c)(2) to require areas
classified as Moderate to provide a 15
percent emission reduction of ozone
precursors within 6 years of the baseline
year. Areas classified as Serious or
higher must meet the RFP requirements
of CAA section 182(c)(2)(B) by
providing an 18 percent reduction of
ozone precursors in the first 6-year
period, and an average ozone precursor
emission reduction of 3 percent per year
for all remaining 3-year periods
thereafter.87 To meet CAA sections
172(c)(2) and 182(c)(2)(B) RFP
requirements, the state may substitute
NOX emissions reductions for VOC
reductions.88
Except as specifically provided in
CAA section 182(b)(1)(C), emissions
reductions from all SIP-approved,
federally promulgated, or otherwise SIPcreditable measures that occur after the
baseline year are creditable for purposes
of demonstrating that the RFP targets are
met. Because the EPA has determined
that the passage of time has caused the
effect of certain exclusions to be de
minimis, the RFP demonstration is no
longer required to calculate and
specifically exclude reductions from
measures related to motor vehicle
exhaust or evaporative emissions
promulgated by January 1, 1990;
regulations concerning Reid vapor
pressure promulgated by November 15,
1990; measures to correct previous
RACT requirements; and, measures
required to correct previous inspection
and maintenance (I/M) programs.89
The 2008 Ozone SRR requires the RFP
baseline year to be the most recent
calendar year for which a complete
triennial inventory was required to be
submitted to the EPA. For the purposes
of developing RFP demonstrations for
the 2008 ozone NAAQS, the applicable
triennial inventory year is 2011. As
discussed previously, the 2008 Ozone
SRR provided states with the
opportunity to use an alternative
baseline year for RFP,90 but that
provision of the 2008 Ozone SRR was
vacated by the D.C. Circuit in the South
Coast II decision.
2. Summary of the State’s Submission
The 2016 Ventura County AQMP
addresses both the ROP (VOC only)
demonstration requirement and the RFP
demonstration requirement. With
respect to the former, the District cites
the EPA’s 1997 approval of the ROP
demonstration for the 1-hour ozone
NAAQS for Ventura County and
concludes that, based on the 1997
approval, the ROP requirement has been
met for Ventura County for the 2008
ozone NAAQS.91
With respect to the RFP
demonstration requirement, the 2016
Ventura County AQMP includes an RFP
demonstration derived from a 2012 RFP
baseline year.92 In response to the South
Coast II decision, CARB developed the
2018 SIP Update, which includes a
section that replaces the RFP portion of
the 2016 Ventura County AQMP and
includes emissions estimates for the
RFP baseline year, subsequent milestone
years, and the attainment year, and an
updated RFP demonstration based on
89 40
86 70
FR 12264, at 12271 (March 6, 2015).
87 Id.
88 40 CFR 51.1110(a)(2)(i)(C) and 40 CFR
51.1110(a)(2)(ii)(B); and 70 FR 12264, at 12271
(March 6, 2015).
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CFR 51.1110(a)(7).
CFR 51.1110(b).
91 See 2016 Ventura County AQMP, 89, and 62 FR
1150 (January 8, 1997).
92 See 2016 Ventura County AQMP, chapter 6
(‘‘Reasonable Further Progress’’).
90 40
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the 2011 RFP baseline year.93 To
develop the 2011 RFP baseline
inventory, CARB relied on actual
emissions reported from industrial point
sources for year 2011. For emissions
from smaller stationary sources and area
sources, CARB backcast emissions from
2012 to 2011 using the same growth and
control factors as were used for the 2016
Ventura County AQMP. To develop the
emissions inventories for the 2017 RFP
milestone year and 2020 RFP milestone/
attainment year, CARB also relied upon
the same growth and control factors as
the 2016 Ventura County AQMP.
Documentation for the Ventura
County RFP baseline and milestone
emissions inventories is found in the
2018 SIP Update on pages 15–18 and
Appendix A on pages A–7 through A–
10. For both sets of baseline emissions
inventories (those in the 2016 Ventura
County AQMP and those in the 2018
SIP Update), emissions estimates reflect
District rules adopted through July 2015
and CARB rules adopted through
November 2015. Unlike the emissions
inventories for the attainment
demonstration in the 2016 Ventura
County AQMP, the RFP baseline and
milestone emissions inventories only
include emissions within the Ventura
County ozone nonattainment area and
do not include marine emissions (e.g.,
emissions from ocean-going vessels)
beyond three nautical miles from the
coastline. In contrast, the attainment
demonstration inventories include
emissions from marine vessels out to
100 nautical miles from the coastline.
Table 3 provides a summary of
CARB’s 2011 RFP baseline year, 2017
RFP milestone year, and 2020 RFP
milestone/attainment year emissions
estimates in tpd for VOC and NOX.
TABLE 3—VENTURA COUNTY 2011 BASE YEAR, 2017 RFP MILESTONE YEAR AND 2020 ATTAINMENT YEAR EMISSIONS
INVENTORIES
[Summer planning inventory, tpd]
2011
2017
2020
Category
VOC
Stationary .................................................................................................
Area Sources ...........................................................................................
On-Road Mobile Sources ........................................................................
Other (Off-Road) Mobile Sources ............................................................
Total (not including ERC balance) ...........................................................
ERC Balance ...........................................................................................
Total (including ERC balance) ..........................................................
VOC
NOX
NOX
8.4
11.7
9.2
8.7
38.1
2.0
1.0
13.9
9.2
26.0
8.4
10.8
5.4
7.2
31.7
1.9
0.7
8.0
7.9
18.5
38.1
26.0
31.7
18.5
VOC
NOX
8.6
11.0
4.2
6.6
30.4
1.7
32.1
1.9
0.6
6.0
7.3
15.8
0.8
16.6
Source: 2018 SIP Update, pp. 15–18 and Appendix A, pp. A–7—A–10. The sum of the emissions values may not equal the total shown due to
rounding of the numbers.
In August 2019, CARB provided a
technical clarification of the RFP
demonstration in the 2018 SIP Update
for Ventura County.94 Specifically,
CARB revised the RFP demonstration in
the 2018 SIP Update to include the
safety margin included in the 2020
motor vehicle emissions budgets in the
2016 Ventura County AQMP. Table 4
presents the updated RFP
demonstration for Ventura County for
the 2008 ozone NAAQS as clarified by
CARB in August 2019.
TABLE 4—RFP DEMONSTRATION FOR VENTURA COUNTY FOR THE 2008 OZONE NAAQS
[Summer planning inventory, tpd or percent]
VOC
Baseline VOC a ...........................................................................................................................
2020 Transportation Conformity Rounding Margin b ..................................................................
Baseline VOC + Rounding Margin .............................................................................................
Required change since 2011 (VOC or NOX), % ........................................................................
Target VOC level ........................................................................................................................
Apparent shortfall (¥)/surplus (+) in VOC .................................................................................
Apparent shortfall (¥)/surplus (+) in VOC, % ............................................................................
VOC shortfall previously provided by NOX substitution, % ........................................................
Actual VOC shortfall (¥)/surplus (+), % .....................................................................................
2011
2017
38.1 ................
........................
........................
........................
........................
........................
........................
........................
........................
31.7 ................
........................
31.7 ................
18% ................
31.2 ................
¥0.5 ..............
¥1.4% ...........
0.0% ...............
¥1.4% ...........
2020
32.1
0.7
32.8
27%
27.8
¥5.0
¥13.2%
1.4%
¥11.7%
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NOX
Baseline NOX a ............................................................................................................................
2020 Transportation Conformity Rounding Margin b ..................................................................
Baseline NOX + Rounding Margin ..............................................................................................
Change in NOX since 2011 ........................................................................................................
Change in NOX since 2011, % ...................................................................................................
NOX reductions used for VOC substitution through last milestone year, % ..............................
NOX reductions since 2011 available for VOC substitution in this milestone year, % ..............
93 2018 SIP Update, RFP demonstration, chapter
III (‘‘SIP Elements for Ventura County’’), section III–
B (‘‘Reasonable Further Progress’’).
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2011
2017
26.0 ................
........................
........................
........................
........................
........................
........................
18.5 ................
........................
18.5 ................
7.5 ..................
28.8% .............
0% ..................
28.8% .............
94 Letter dated August 29, 2019, from Dr. Michael
T. Benjamin, Chief, Air Quality Planning and
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2020
16.6
0.9
17.5
8.5
32.8%
1.4%
31.4%
Science Division, CARB, to Amy Zimpfer, Assistant
Director, Air Division, EPA Region IX.
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NOX
NOX reductions since 2011 used for VOC substitution in this milestone year, % .....................
NOX reductions since 2011 surplus after meeting VOC substitution needs in this milestone
year, %.
Total shortfall for RFP .................................................................................................................
RFP met? ....................................................................................................................................
2011
2017
2020
........................
........................
1.4% ...............
27.4% .............
11.7%
19.6%
........................
........................
0% ..................
Yes .................
0%
Yes
Source: Letter dated August 29, 2019, from Dr. Michael T. Benjamin, Chief, Air Quality Planning and Science Division, CARB, to Amy Zimpfer,
Assistant Director, Air Division, EPA Region IX, Attachment A.
a 2020 projections include addition of ERC balance as of January 1, 2012.
b Transportation conformity rounding margin is referred to herein as a ‘‘safety margin.’’
The revised RFP demonstration
calculates future year VOC targets from
the 2011 baseline, consistent with CAA
182(c)(2)(B)(i), which requires
reductions of ‘‘at least 3 percent of
baseline emissions each year;’’ and it
substitutes NOX reductions for VOC
reductions beginning in milestone year
2017 to meet VOC emission targets.95
For Ventura County, CARB concludes
that the revised RFP demonstration
meets the applicable requirements for
each milestone year as well as the
attainment year.
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3. The EPA’s Review of the State’s
Submission
In 1997, the EPA approved a 15
percent ROP plan for the Ventura
County ozone nonattainment area for
the 1-hour ozone NAAQS, and the
Ventura County nonattainment area for
the 2008 ozone NAAQS is the same as
the Ventura County nonattainment area
for the 1-hour ozone NAAQS.96 As a
result, we agree with the District that
the District and CARB have met the ROP
requirements of CAA section 182(b)(1)
for Ventura County with respect to the
2008 ozone NAAQS.
With respect to the RFP
demonstration requirement, based on
our review of the emissions inventory
documentation in the 2016 Ventura
County Ozone SIP, we find that CARB
and the District have used the most
recent planning and activity
assumptions, emissions models, and
methodologies in developing the RFP
baseline and milestone year emissions
inventories. We have also reviewed the
calculations in Table III–3 of the 2018
SIP Update, as clarified by CARB in
August 2019, and find that CARB has
used an appropriate calculation method
to demonstrate RFP.97 For these reasons,
95 NO substitution is permitted under EPA
X
regulations. See 40 CFR 51.1110(a)(2)(i)(C) and 40
CFR 51.1110(a)(2)(ii)(B); and 70 FR 12264, at 12271
(March 6, 2015).
96 62 FR 1150, at 1183 (January 8, 1997).
97 We note a minor discrepancy between the
safety margins included in the revised RFP
demonstration for the 2020 attainment year and the
safety margins included in the motor vehicle
emissions budgets for 2020 in the 2016 Ventura
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we have determined that the 2016
Ventura County Ozone SIP, as clarified
by CARB in August 2019, demonstrates
RFP in the 2017 milestone year and the
2020 milestone/attainment year,
consistent with applicable CAA
requirements and EPA guidance.
Therefore, we propose to approve the
RFP demonstration for Ventura County
for the 2008 ozone NAAQS under
sections 172(c)(2) and 182(c)(2)(B) of the
CAA and 40 CFR 51.1110(a)(2)(ii).
F. Contingency Measures
1. Statutory and Regulatory
Requirements
Under the CAA, 8-hour ozone
nonattainment areas classified under
subpart 2 as Moderate or above must
include in their SIPs contingency
measures consistent with sections
172(c)(9) and 182(c)(9). Contingency
measures are additional controls or
measures to be implemented in the
event the area fails to make reasonable
further progress or to attain the NAAQS
by the attainment date. The SIP should
contain trigger mechanisms for the
contingency measures, specify a
schedule for implementation, and
indicate that the measure will be
implemented without significant further
action by the state or the EPA.98
Neither the CAA nor the EPA’s
implementing regulations establish a
specific level of emissions reductions
that implementation of contingency
measures must achieve, but the EPA’s
2008 Ozone SRR reiterates the EPA’s
policy that contingency measures
County AQMP. The safety margins for the RFP
demonstration, as shown in Table 4 of this
document, are 0.7 tpd for VOC and 0.9 tpd for NOX.
The safety margins for the motor vehicle emissions
budgets in the 2016 Ventura County AQMP are 0.79
tpd for VOC (0.8 tpd, if rounded to one significant
figure) and 0.99 tpd (1.0 tpd, if rounded). Given the
substantial extent to which the 2016 Ventura
County Ozone SIP provides emissions reductions in
excess of the RFP milestones, this minor
discrepancy does not change our proposed finding
that the 2016 Ventura County Ozone SIP meets the
RFP demonstration requirement for the 2008 ozone
NAAQS.
98 70 FR 71612 (November 29, 2005). See also
2008 Ozone SRR, 80 FR 12264, at 12285 (March 6,
2015).
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should provide for emissions reductions
approximately equivalent to one year’s
worth of progress, amounting to
reductions of 3 percent of the RFP
baseline emissions inventory for the
nonattainment area.99
It has been the EPA’s longstanding
interpretation of section 172(c)(9) that
states may rely on federal measures
(e.g., federal mobile source measures
based on the incremental turnover of the
motor vehicle fleet each year) and local
measures already scheduled for
implementation that provide emissions
reductions in excess of those needed to
provide for RFP or expeditious
attainment. The key is that the statute
requires that contingency measures
provide for additional emissions
reductions that are not relied on for RFP
or attainment and that are not included
in the RFP or attainment
demonstrations. The purpose of
contingency measures is to provide
continued emissions reductions while
the plan is being revised to meet the
missed milestone or attainment date.
The EPA has approved numerous SIPs
under this interpretation—i.e., SIPs that
use as contingency measures one or
more federal or local measures that are
in place and provide reductions that are
in excess of the reductions required by
the attainment demonstration or RFP
plan,100 and there is case law
supporting the EPA’s interpretation in
this regard.101 However, in Bahr v. EPA,
the Ninth Circuit rejected the EPA’s
interpretation of CAA section 172(c)(9)
as allowing for early implementation of
99 80
FR 12264, at 12285 (March 6, 2015).
e.g., 62 FR 15844 (April 3, 1997) (direct
final rule approving an Indiana ozone SIP revision);
62 FR 66279 (December 18, 1997) (final rule
approving an Illinois ozone SIP revision); 66 FR
30811 (June 8, 2001) (direct final rule approving a
Rhode Island ozone SIP revision); 66 FR 586
(January 3, 2001) (final rule approving District of
Columbia, Maryland, and Virginia ozone SIP
revisions); and 66 FR 634 (January 3, 2001) (final
rule approving a Connecticut ozone SIP revision).
101 See, e.g., LEAN v. EPA, 382 F.3d 575 (5th Cir.
2004) (upholding contingency measures that were
previously required and implemented where they
were in excess of the attainment demonstration and
RFP SIP).
100 See,
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contingency measures.102 The Ninth
Circuit concluded that contingency
measures must take effect at the time the
area fails to make RFP or attain by the
applicable attainment date, not
before.103 Thus, within the geographic
jurisdiction of the Ninth Circuit, states
cannot rely on early-implemented
measures to comply with the
contingency measure requirements
under CAA section 172(c)(9) and
182(c)(9).104
2. Summary of the State’s Submission
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The District and CARB had largely
prepared the 2016 Ventura County
Ozone SIP prior to the Bahr v. EPA
decision, and thus, consistent with
contingency measure elements of
previous ozone plans, it relies solely
upon surplus emissions reductions from
already-implemented control measures
to demonstrate compliance with the
contingency measure requirements of
CAA sections 172(c)(9) and 182(c)(9).105
In the 2018 SIP Update, CARB revises
the RFP demonstration for the 2008
ozone NAAQS for Ventura County and
recalculates the extent of surplus
emission reductions (i.e., surplus to
meeting the RFP milestone requirement
for a given milestone year) in the
milestone years and estimates the
incremental emissions reductions in the
year following the attainment year. In
light of the Bahr v. EPA decision,
however, the 2018 SIP Update does not
rely on the surplus or incremental
emissions reductions to comply with
the contingency measures requirements
of sections 172(c)(9) and 182(c)(9) but,
rather, to provide context in which to
evaluate the adequacy of Bahrcompliant (i.e., to take effect if triggered)
contingency measures for the 2008
ozone NAAQS.106
To comply with CAA sections
172(c)(9) and 182(c)(9), as interpreted in
the Bahr v. EPA decision, the state must
develop, adopt, and submit a
contingency measure to be triggered
upon a failure to meet an RFP milestone
or attain the NAAQS by the applicable
attainment date regardless of the extent
102 Bahr v. EPA, 836 F.3d 1218, at 1235–1237 (9th
Cir. 2016).
103 Id. at 1235–1237.
104 The Bahr v. EPA decision involved a challenge
to an EPA approval of contingency measures under
the general nonattainment area plan provisions for
contingency measures in CAA section 172(c)(9),
but, given the similarity between the statutory
language in section 172(c)(9) and the ozone-specific
contingency measure provision in section 182(c)(9),
we find that the decision affects how both sections
of the Act must be interpreted.
105 2016 Ventura County AQMP, chapter 7
(‘‘Contingency Measures’’), 91 and 92.
106 2018 SIP Update, chapter III (‘‘SIP Elements
for Ventura County’’), 18–20.
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element of the 2016 Ventura County
Ozone SIP.108
to which already-implemented
measures would achieve surplus or
incremental emissions reductions
beyond those necessary for RFP or
attainment of the NAAQS. Therefore, to
fully address the contingency measure
requirement for the 2008 ozone NAAQS
in Ventura County, the District has
committed to supplement the
contingency measure element of the
2016 Ventura County Ozone SIP by
developing, adopting and submitting a
contingency measure to CARB in
sufficient time to allow CARB to submit
the contingency measure as a SIP
revision to the EPA within 12 months of
the EPA’s conditional approval of the
contingency measure element of the
2016 Ventura County Ozone SIP.107
The District’s specific commitment is
to amend at least one of the following
existing VCAPCD rules, through the
required public review and subsequent
VCAPCD board approval processes, to
apply more stringent requirements upon
a determination that the Ventura County
nonattainment area failed to meet an
RFP milestone or failed to attain the
2008 ozone NAAQS by the applicable
attainment date.
• Amendments to Rule 74.26 (‘‘Crude
Oil Storage Tank Degassing
Operations’’) to add, if triggered by an
RFP milestone failure or a failure to
attain the 2008 ozone NAAQS,
requirements for reducing VOC
emissions from certain operations not
covered by the existing rule, including
cleaning, removing, repair and
depressurizing of pipelines;
• Amendments to Rule 74.14
(‘‘Polyester Resin Material Operations’’)
to add a non-monomer content VOC
limit of no more than 5 percent by
weight, if triggered; or
• Amendments to Rule 74.2
(‘‘Architectural Coatings’’) to lower the
VOC limit for coating categories; delete
the Specialty Primer, Sealer, and
Undercoater categories and regulate
them as just primers, sealers and
undercoaters; add the specialty coating
categories (Interior Stains, and Tile and
Stone Sealers); and lower certain VOC
content limits for colorants, once again,
if triggered.
CARB attached the District’s
commitment to revise a rule to include
contingency provisions to a letter
committing CARB to adopt and submit
the revised VCAPCD rule or rules to the
EPA within one year of the effective
date of the EPA’s final conditional
approval of the contingency measure
3. The EPA’s Review of the State’s
Submission
Sections 172(c)(9) and 182(c)(9)
require contingency measures to address
potential failure to achieve RFP
milestones or failure to attain the
NAAQS by the applicable attainment
date. For the purposes of evaluating the
contingency measure element of the
2016 Ventura County Ozone SIP, we
find it useful to distinguish between
contingency measures to address
potential failure to achieve RFP
milestones (‘‘RFP contingency
measures’’) and contingency measures
to address potential failure to attain the
NAAQS (‘‘attainment contingency
measures’’).
With respect to the RFP contingency
measure requirement, we have reviewed
the surplus emissions estimates in each
of the RFP milestone years, as shown in
the 2018 SIP Update (and clarified in
August 2019), and find that the
calculations are correct. Therefore, we
agree that the 2016 Ventura County
Ozone SIP provides surplus emissions
reductions well beyond those necessary
to demonstrate RFP in the RFP
milestone years. While such surplus
emissions reductions in the RFP
milestone years do not represent
contingency measures themselves, we
believe they are relevant in evaluating
the adequacy of RFP contingency
measures that are submitted (or will be
submitted) to meet the requirements of
sections 172(c)(9) and 182(c)(9).
In this case, the District and CARB
have committed to develop, adopt, and
submit a revised District rule or rules as
a contingency measure within one year
of the effective date of our final
conditional approval action. The
specific types of revisions the District
has committed to make, such as adding
new limits or other requirements, upon
a failure to achieve a milestone or a
failure to attain would comply with the
requirements in CAA sections 172(c)(9)
and 182(c)(9) because they would be
undertaken if the area fails to attain and
would take effect without significant
further action by the State or the EPA.
Next, we considered the adequacy of
the RFP contingency measure (once
adopted and submitted) from the
standpoint of the magnitude of
emissions reductions the measure
would provide (if triggered). Neither the
CAA nor the EPA’s implementing
regulations for the ozone NAAQS
107 Letter dated August 16, 2019, from Michael
Villegas, Air Pollution Control Officer, VCAPCD, to
Richard Corey, Executive Officer, CARB.
108 Letter dated August 30, 2019, from Richard W.
Corey, Executive Officer, CARB, to Mike Stoker,
Regional Administrator, EPA Region IX.
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establish a specific amount of emissions
reductions that implementation of
contingency measures must achieve, but
we generally expect that contingency
measures should provide for emissions
reductions approximately equivalent to
one year’s worth of RFP, which, for
ozone, amounts to reductions of 3
percent of the RFP baseline year
emissions inventory for the
nonattainment area. For the 2008 ozone
NAAQS in Ventura County, one year’s
worth of RFP is approximately 1.1 tpd
of VOC or 0.8 tpd of NOX reductions.109
The District did not quantify the
potential additional emission reductions
from its contingency measure
commitment, but we believe that it is
unlikely that the attainment
contingency measure, once adopted and
submitted, will achieve one year’s worth
of RFP (i.e., 1.1 tpd of VOC or 0.8 tpd
of NOX) given the types of rule revisions
under consideration and the magnitude
of emissions reductions constituting one
year’s worth of RFP. However, the 2018
SIP Update provides the larger SIP
planning context in which to judge the
adequacy of the to-be-submitted District
contingency measure by calculating the
surplus emissions reductions estimated
to be achieved in the RFP milestone
years and the year after the attainment
year. More specifically, the 2018 SIP
Update, as clarified by CARB in August
2019, identified surplus NOX reductions
in the various RFP milestone years. For
Ventura County, the estimates of
surplus NOX reductions are 7.1 tpd in
2017 and 6.5 tpd in 2020 and are 8 or
9 times greater than one year’s worth of
progress (0.8 tpd of NOX).110
The surplus reflects already
implemented regulations and is
primarily the result of vehicle turnover,
which refers to the ongoing replacement
by individuals, companies, and
government agencies of older, more
polluting vehicles and engines with
newer vehicles and engines. In light of
the extent of surplus NOX emissions
reductions in the RFP milestone years,
the emissions reductions from the
District contingency measure would be
sufficient to meet the contingency
measure requirements of the CAA with
respect to RFP milestones, even though
the measure would likely achieve
emissions reductions lower than the
EPA normally recommends for
reductions from such a measure.
109 One year’s worth of RFP for Ventura County
corresponds to 3 percent of the RFP baseline year
inventories for VOC (38.1 tpd) and NOX (26.0 tpd).
110 For the 2017 and 2020 RFP milestone years,
surplus NOX reductions correspond to 27.4 percent
and 24.9 percent, respectively, of the 26.0 tpd 2011
RFP milestone inventory. See Table 4 in section
III.E of this document.
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For attainment contingency measure
purposes, we view the emissions
reductions from the contingency
measure in the context of the expected
reduction in emissions within Ventura
County in the year following the
attainment year relative to those
occuring in the attainment year. Based
on the emission inventories in
Appendix A to the 2018 SIP Update, we
note that overall county-wide emissions
are expected to be approximately 0.9
tpd of NOX lower in 2021 than in 2020.
Thus, baseline measures are expected to
provide for continued progress (i.e.,
incremental reduction in ozone
precursors) greater than one year’s
worth of progress (i.e., 0.8 tpd of NOX).
In light of these incremental year-overyear NOX emissions reductions, we find
that the emissions reductions from the
District contingency measure would
also be sufficient to meet the attainment
contingency measure requirement of the
CAA, even though the measure would
likely achieve emissions reductions
lower than the EPA normally
recommends for reductions from such a
measure.
For these reasons, we propose to
approve conditionally the contingency
measure element of the 2016 Ventura
County Ozone SIP, as supplemented by
commitments from the District and
CARB to adopt and submit an additional
contingency measure, to meet the
contingency measure requirements of
CAA sections 172(c)(9) and 182(c)(9).
Our proposed approval is conditional
because it relies upon commitments to
adopt and submit a specific enforceable
contingency measure (i.e., a revised
District rule or rules with contingent
provisions). Conditional approvals are
authorized under CAA section 110(k)(4).
G. Motor Vehicle Emissions Budgets for
Transportation Conformity
1. Statutory and Regulatory
Requirements
Section 176(c) of the CAA requires
federal actions in nonattainment and
maintenance areas to conform to the
SIP’s goals of eliminating or reducing
the severity and number of violations of
the NAAQS and achieving timely
attainment of the standards. Conformity
to the SIP’s goals means that such
actions will not: (1) Cause or contribute
to violations of a NAAQS, (2) worsen
the severity of an existing violation, or
(3) delay timely attainment of any
NAAQS or any interim milestone.
Actions involving Federal Highway
Administration (FHWA) or Federal
Transit Administration (FTA) funding
or approval are subject to the EPA’s
transportation conformity rule, codified
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70125
at 40 CFR part 93, subpart A. Under this
rule, MPOs in nonattainment and
maintenance areas coordinate with state
and local air quality and transportation
agencies, the EPA, the FHWA, and the
FTA to demonstrate that an area’s
regional transportation plans and
transportation improvement programs
conform to the applicable SIP. This
demonstration is typically done by
showing that estimated emissions from
existing and planned highway and
transit systems are less than or equal to
the motor vehicle emissions budgets
(‘‘budgets’’) contained in all control
strategy SIPs. Budgets are generally
established for specific years and
specific pollutants or precursors. Ozone
plans should identify budgets for onroad emissions of ozone precursors
(NOX and VOC) in the area for each RFP
milestone year and, if the plan
demonstrates attainment, the attainment
year.111
For budgets to be approvable, they
must meet, at a minimum, the EPA’s
adequacy criteria (40 CFR 93.118(e)(4)).
To meet these requirements, the budgets
must be consistent with the attainment
and RFP requirements and reflect all of
the motor vehicle control measures
contained in the attainment and RFP
demonstrations.112
The EPA’s process for determining
adequacy of a budget consists of three
basic steps: (1) Providing public
notification of a SIP submission; (2)
providing the public the opportunity to
comment on the budget during a public
comment period; and, (3) making a
finding of adequacy or inadequacy.113
2. Summary of the State’s Submission
The 2016 Ventura County AQMP
includes budgets for the 2018 RFP
milestone year and the 2020 attainment
year.114 The budgets for 2018 were
derived from the 2012 RFP baseline year
and the associated 2018 RFP milestone
year. As such, the budgets are affected
by the South Coast II decision vacating
111 40
CFR 93.102(b)(2)(i).
CFR 93.118(e)(4)(iii), (iv) and (v). For more
information on the transportation conformity
requirements and applicable policies on budgets,
please visit our transportation conformity website
at: https://www.epa.gov/otaq/stateresources/
transconf/index.htm.
113 40 CFR 93.118(f)(2).
114 When the 2016 Ventura County AQMP was
developed, 2012 was used as the RFP baseline year,
and 2020 was not considered an RFP milestone year
because it was not one of the years that follow in
the three-year cycle after the initial six-year period
after the RFP baseline year. However, in the wake
of the South Coast II decision, 2011 became the
required RFP baseline year and year 2020 became
an RFP milestone year because it is three years after
the initial six-year period from the 2011 RFP
baseline year. Thus, the 2020 budgets from the 2016
Ventura County AQMP now serve as both the RFP
milestone and attainment budgets.
112 40
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the alternative baseline year provision,
and therefore, the EPA has not
previously acted on the budgets. In the
submittal letter for the 2016 Ventura
County AQMP, CARB requested that the
EPA limit the duration of our approval
of the budgets in the 2016 Ventura
County AQMP to last only until the
effective date of future EPA adequacy
findings for replacement budgets.115 In
August 2019, CARB provided further
explanation in connection with its
request to limit the duration of the
approval of the budgets in the 2016
Ventura County AQMP.116
On December 5, 2018, CARB
submitted the 2018 SIP Update, which
revised the RFP demonstration
consistent with the South Coast II
decision (i.e., by using a 2011 RFP
baseline year). The 2018 SIP Update
does not identify new budgets for
Ventura County for VOC and NOX for
the 2017 RFP milestone year because
budgets for the 2017 milestone year
would never be used for conformity
determinations given that milestone/
attainment budgets for the immediate
near-term year of 2020 have also been
submitted. Today, we are proposing
action only on the 2020 RFP milestone/
attainment budgets from the 2016
Ventura County AQMP.
The budgets in the 2016 Ventura
County AQMP were derived from motor
vehicle emissions estimates prepared
using EMFAC2014,117 and the travel
activity data provided by SCAG. The
conformity budgets for NOX and VOC in
the 2016 Ventura County AQMP for
Ventura County in 2020 are provided in
Table 5 below. To develop the budgets,
the District rounded up the motor
vehicle emissions estimates for 2020 to
the nearest ton. Thus, the motor vehicle
emissions estimates for Ventura County
for VOC and NOX in 2020, i.e., 4.21 tpd
and 6.01 tpd, respectively, were
rounded up to become budgets for VOC
and NOX of 5 tpd and 7 tpd,
respectively.
115 Letter dated April 11, 2017, from Richard
Corey, Executive Officer, CARB, to Alexis Strauss,
Acting Regional Administrator, EPA Region IX,
transmitting the 2016 Ventura County AQMP.
116 Letter dated August 29, 2019, from Dr.
Michael T. Benjamin, Chief, Air Quality Planning
and Science Division, CARB, to Amy Zimpfer,
Assistant Director, Air Division, EPA Region IX.
117 As previously noted, EMFAC2014 is CARB’s
model for estimating emissions from on-road
vehicles operating in California. See 80 FR 77337
(December 14, 2015). We have recently announced
the availability of an updated version of EMFAC,
referred to as EMFAC2017. See 84 FR 41717
(August 15, 2019). For the 2016 Ventura County
Ozone SIP, EMFAC2014 was the appropriate model
to use for SIP development purposes at the time it
was prepared.
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TABLE 5—TRANSPORTATION CONFORMITY BUDGETS FOR THE 2008
OZONE NAAQS IN VENTURA COUNTY
[Summer planning inventory, tpd]
Budget year
VOC
NOX
2020 ..........................
5
7
Source: 2016 Ventura County AQMP, Table
3–7, 52.
3. The EPA’s Review of the State’s
Submission
As part of our review of the
approvability of the budgets in the 2016
Ventura County AQMP, we have
evaluated the budgets using our
adequacy criteria in 40 CFR 93.118(e)(4)
and (5). We will complete the adequacy
review concurrent with our final action
on the 2016 Ventura County AQMP. The
EPA is not required under its
transportation conformity rule to find
budgets adequate prior to proposing
approval of them.118 Today, the EPA is
announcing that the adequacy process
for these budgets begins, and the public
has 30 days to comment on their
adequacy, per the transportation
conformity regulation at 40 CFR
93.118(f)(2)(i) and (ii).
As documented in a separate
memorandum included in the docket for
this rulemaking, we preliminarily
conclude that the budgets in the 2016
Ventura County AQMP meet each
adequacy criterion.119 While adequacy
and approval are two separate actions,
reviewing the budgets in terms of the
adequacy criteria informs the EPA’s
decision to propose to approve the
budgets. We have completed our
detailed review of the 2016 Ventura
County AQMP and are proposing herein
to approve the attainment and RFP
demonstrations. We have also reviewed
the budgets in the 2016 Ventura County
AQMP and found that they are
consistent with the attainment and RFP
demonstrations for which we are
proposing approval, are based on
control measures that have already been
adopted and implemented, and meet all
other applicable statutory and
regulatory requirements including the
adequacy criteria in 40 CFR
118 Under the transportation conformity
regulations, the EPA may review the adequacy of
submitted motor vehicle emission budgets
simultaneously with the EPA’s approval or
disapproval of the submitted implementation plan.
40 CFR 93.118(f)(2).
119 Memorandum dated September 5, 2019, from
John J. Kelly, Air Planning Office, EPA Region 9,
to docket for this proposed rulemaking, titled
‘‘Adequacy Documentation for Plan Motor Vehicle
Emission Budgets in 2016 Ventura County Ozone
Plan.’’
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93.1118(e)(4) and (5). Therefore, we are
proposing to approve the 2020 budgets
in the 2016 Ventura County AQMP. At
the point when we either finalize the
adequacy process or approve the
budgets for the 2008 ozone NAAQS in
the 2016 Ventura County AQMP as
proposed (whichever occurs first; note
that they could also occur concurrently
per 40 CFR 93.118(f)(2)(iii)), they will
replace the budgets that we previously
found adequate for use in transportation
conformity determinations.120
Under our transportation conformity
rule, as a general matter, once budgets
are approved, they cannot be
superseded by revised budgets
submitted for the same CAA purpose
and the same year(s) addressed by the
previously approved SIP until the EPA
approves the revised budgets as a SIP
revision. In other words, as a general
matter, such approved budgets cannot
be superseded by revised budgets found
adequate, but rather only through
approval of the revised budgets, unless
the EPA specifies otherwise in its
approval of a SIP by limiting the
duration of the approval to last only
until subsequently submitted budgets
are found adequate.121
In this instance, as noted above, in its
submittal letter, CARB requested that
we limit the duration of our approval of
the budgets in the 2016 Ventura County
AQMP only until the effective date of
the EPA’s adequacy finding for
subsequently submitted budgets, and in
August 2019, CARB provided further
explanation for its request. Generally,
we will consider a state’s request to
limit an approval of a budget only if the
request includes the following
elements: 122
• An acknowledgement and
explanation as to why the budgets under
consideration have become outdated or
deficient;
• A commitment to update the
budgets as part of a comprehensive SIP
update; and
• A request that the EPA limit the
duration of its approval to the time
when new budgets have been found to
be adequate for transportation
conformity purposes.
CARB’s request includes an
explanation for why the budgets have
become, or will become, outdated or
deficient. In short, CARB requested that
120 In May 2008, we found adequate the 2009
budgets from the Ventura County 2008 8-hour
Ozone Early Progress Plan (February 2008). 73 FR
24595 (May 5, 2008). The 2009 budgets are 13 tpd
for VOC and 19 tpd for NOX.
121 40 CFR 93.118(e)(1).
122 67 FR 69139 (November 15, 2002) (final action
limiting our prior approval of budgets in certain
California SIPs).
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we limit the duration of the approval of
the budgets in light of the EPA’s recent
approval of EMFAC2017, an updated
version of the model (EMFAC2014) used
for the budgets in the 2016 Ventura
County AQMP. EMFAC2017 updates
vehicle mix and emissions data of the
previously approved version of the
model, EMFAC2014.
Preliminary calculations by CARB
indicate that EMFAC2017-derived
motor vehicle emissions estimates for
Ventura County will exceed the
corresponding EMFAC2014-derived
budgets in the 2016 Ventura County
AQMP. In light of the approval of
EMFAC2017, CARB explains that the
budgets from the 2016 Ventura County
AQMP, for which we are proposing
approval in today’s action, will become
outdated and will need to be revised
using EMFAC2017. In addition, CARB
states that, without the ability to replace
the budgets using the budget adequacy
process, the benefits of using the
updated data may not be realized for a
year or more after the updated SIP (with
the EMFAC2017-derived budgets) is
submitted, due to the length of the SIP
approval process. We find that CARB’s
explanation for limiting the duration of
the approval of the budgets is
appropriate and provides us with a
reasonable basis on which to limit the
duration of the approval of the budgets.
We note that CARB has not
committed to update the budgets as part
of a comprehensive SIP update, but as
a practical matter, CARB must submit a
SIP revision that includes updated
demonstrations as well as the updated
budgets to meet the adequacy criteria in
40 CFR 93.118(e)(4); 123 and thus, we do
not need a specific commitment for
such a plan at this time. For the reasons
provided above, and in light of CARB’s
explanation for why the budgets will
become outdated and should be
replaced upon an adequacy finding for
updated budgets, we propose to limit
the duration of our approval of the
budgets in the 2016 Ventura County
AQMP until we find revised budgets
based on EMFAC2017 to be adequate.
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H. General Conformity Budgets
1. Statutory and Regulatory
Requirements
Section 176(c) of the CAA requires
federal actions in nonattainment and
maintenance areas to conform to the
SIP’s goals of eliminating or reducing
123 Under 40 CFR 93.118(e)(4), the EPA will not
find a budget in a submitted SIP to be adequate
unless, among other criteria, the budgets, when
considered together with all other emissions
sources, are consistent with applicable
requirements for RFP and attainment. 40 CFR
93.118(e)(4)(iv).
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the severity and number of violations of
the NAAQS and achieving timely
attainment of the standards. Conformity
to the SIP’s goals means that such
actions will not: (1) Cause or contribute
to violations of a NAAQS, (2) worsen
the severity of an existing violation, or
(3) delay timely attainment of any
NAAQS or any interim milestone.
Section 176(c)(4) of the CAA
establishes the framework for general
conformity. The EPA first promulgated
general conformity regulations in
November 1993.124 On April 5, 2010,
the EPA revised the general conformity
regulations.125 The general conformity
regulations ensure that federal actions
not covered by the transportation
conformity rule will not interfere with
the SIP and encourage consultation
between the federal agency and the state
or local air pollution control agencies
before or during the environmental
review process, as well as public
participation (e.g., notification of and
access to federal agency conformity
determinations and review of individual
federal actions).
The general conformity regulations
provide three phases: Applicability
analysis, conformity determination, and
review process. The applicability
analysis phase under 40 CFR 93.153 is
used to find if a federal action requires
a conformity determination for a
specific pollutant. If a conformity
determination is needed, federal
agencies can use one of several methods
to show that the federal action conforms
to the SIP. In an area without a SIP, a
federal action may be shown to
‘‘conform’’ by demonstrating there will
be no net increase in emissions in the
nonattainment or maintenance area
from the federal action. In an area with
a SIP, conformity to the applicable SIP
can be demonstrated in one of several
ways. For actions where the direct and
indirect emissions exceed the rates in 40
CFR 93.153(b), the federal action can
include mitigation measures to offset
the emission increases from the federal
action or can show that the action will
conform by meeting any of the following
requirements:
• Showing that the net emission
increases caused by an action are
included in the SIP,
• documenting that the state agrees to
include the emission increases in the
SIP,
• offsetting the action’s emissions in
the same or nearby area of equal or
greater classification, or
124 40 CFR part 51, subpart W, and 40 CFR part
93, subpart B.
125 75 FR 17254.
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• providing an air quality modeling
demonstration in some
circumstances.126
The general conformity regulations at
40 CFR 93.161 allow state and local air
quality agencies working with federal
agencies with large facilities (e.g.,
commercial airports, ports, and large
military bases) that are subject to the
general conformity regulations to
develop and adopt an emissions budget
for those facilities in order to facilitate
future conformity determinations. Such
a budget, referred to as a facility-wide
emissions budget, may be used by
federal agencies to demonstrate
conformity as long as the total facilitywide budget level identified in the SIP
is not exceeded.
According to 40 CFR 93.161, the state
or local agency responsible for
implementing and enforcing the SIP can
develop and adopt an emissions budget
to be used for demonstrating conformity
under 40 CFR 93.158(a)(1). The
requirements include the following: (1)
The facility-wide budget must be for a
set time period; (2) the budget must
cover the pollutants or precursors of the
pollutants for which the area is
designated nonattainment or
maintenance; (3) the budgets must be
specific about what can be emitted on
an annual or seasonal basis; (4) the
emissions from the facility along with
all other emissions in the area must not
exceed the total SIP emissions budget
for the nonattainment or maintenance
area; (5) specific measures must be
included to ensure compliance with the
facility-wide budget, such as periodic
reporting requirements or compliance
demonstrations when the federal agency
is taking an action that would otherwise
require a conformity determination; (6)
the budget must be submitted to the
EPA as a SIP revision; and (7) the SIP
revision must be approved by the EPA.
Having or using a facility-wide
emissions budget does not preclude a
federal agency from demonstrating
conformity in any other manner allowed
by the conformity rule.
2. Summary of the State’s Submission
The 2016 Ventura County AQMP
establishes VOC and NOX general
conformity budgets for the Naval Base
Ventura County (NBVC) for each year
from 2017 through 2020 as shown in
Table 6 below. The budgets are intended
to reflect aircraft and missile operations
associated with NBVC Point Mugu and
ship operations at Port Hueneme
occuring within the Ventura County
126 40 CFR 93.158; and VCAPCD Rule 220
(‘‘General Conformity’’), approved at 64 FR 19916
(April 23, 1999).
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ozone nonattainment area. The budgets
include a 4 percent growth allowance to
account for uncertainties in potential
projects resulting from future actions
and unknown projects. As shown in
Table 6, the budgets for NBVC in the
attainment year (2020) are 198.0 tpy of
VOC and 475.9 tpy of NOX, which is
equivalent to 0.54 tpd of VOC and 1.30
tpd of NOX on an annual average daily
basis.
TABLE 6—NBVC GENERAL CONFORMITY BUDGETS FOR THE 2008
OZONE NAAQS IN VENTURA COUNTY
[summer planning inventory, tpy]
Budget year
2017
2018
2019
2020
VOC
..........................
..........................
..........................
..........................
Source: 2016 Ventura
AQMP, Table 4–9.
NOX
178.6
184.8
191.3
198.0
County
434.2
447.6
461.5
475.9
Ozone
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3. The EPA’s Review of the State’s
Submission
We propose to approve the general
conformity budgets in the 2016 Ventura
County AQMP for NBVC shown in
Table 6, as meeting the requirements of
CAA section 176(c) and 40 CFR 93.161.
We find that the general conformity
budgets in the 2016 AQMP: are
established for a set time period; cover
both precursors of ozone; are precisely
quantified in terms of tons per year;
and, along with all other emissions in
Ventura County, are consistent with the
RFP and attainment demonstration for
the 2008 ozone NAAQS.
If we finalize our approval of these
budgets, NBVC can use these budgets to
demonstrate that their projects conform
to the SIP through a letter from the State
and District confirming that the project
emissions are accounted for in the SIP’s
general conformity budgets.
I. Other Clean Air Act Requirements
Applicable to Serious Ozone
Nonattainment Areas
In addition to the SIP requirements
discussed in the previous sections, the
CAA includes certain other SIP
requirements applicable to Serious
ozone nonattainment areas, such as
Ventura County. We describe these
provisions and their current status
below.
1. Enhanced Vehicle Inspection and
Maintenance Programs
Section 182(c)(3) of the CAA requires
states with ozone nonattainment areas
classified under subpart 2 as Serious or
above to implement an enhanced motor
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vehicle I/M program in those areas. The
requirements for those programs are
provided in CAA section 182(c)(3) and
40 CFR part 51, subpart S.
Consistent with the 2008 Ozone SRR,
no new I/M programs are currently
required for nonattainment areas for the
2008 ozone NAAQS.127 The EPA
previously approved California’s I/M
program in Ventura County as meeting
the requirements of the CAA and
applicable EPA regulations for
enhanced I/M programs.128
2. New Source Review Rules
Section 182(a)(2)(C) of the CAA
requires states to develop SIP revisions
containing permit programs for each of
its ozone nonattainment areas. The SIP
revisions are to include requirements for
permits in accordance with CAA
sections 172(c)(5) and 173 for the
construction and operation of each new
or modified major stationary source for
VOC and NOX anywhere in the
nonattainment area. The 2008 Ozone
SRR includes provisions and guidance
for nonattainment NSR programs.129
Earlier this year, the EPA proposed to
approve the nonattainment NSR SIP
submitted for Ventura County for the
2008 ozone NAAQS. The nonattainment
NSR SIP includes a certification letter
documenting how the VCAPCD’s SIPapproved nonattainment NSR program,
established in VCAPCD Rules 26
through 26.11, meets the applicable
NSR requirements for Ventura County
for the 2008 ozone NAAQS.130 We
expect to take final action on the
nonattainment NSR SIP for Ventura
County for the 2008 ozone NAAQS in
the near future in a separate rulemaking.
3. Clean Fuels Fleet Program
Sections 182(c)(4)(A) and 246 of the
CAA require California to submit to the
EPA for approval measures to
implement a Clean Fuels Fleet Program.
Section 182(c)(4)(B) of the CAA allows
states to opt-out of the federal clean-fuel
vehicle fleet program by submitting a
SIP revision consisting of a program or
programs that will result in at least
equivalent long-term reductions in
ozone precursors and toxic air
emissions.
In 1994, CARB submitted a SIP
revision to the EPA to opt-out of the
federal clean-fuel fleet program. The
submittal included a demonstration that
California’s low-emissions vehicle
program achieved emissions reductions
127 2008 Ozone SRR, 80 FR 12264, at 12283
(March 6, 2015).
128 75 FR 38023 (July 1, 2010).
129 80 FR 12264 (March 6, 2015).
130 84 FR 20604 (May 10, 2019); reproposed at 84
FR 43738 (August 22, 2019).
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at least as large as would be achieved by
the federal program. The EPA approved
the SIP revision to opt-out of the federal
program on August 27, 1999.131 There
have been no changes to the federal
Clean Fuels Fleet program since the
EPA approved the California SIP
revision to opt-out of the federal
program, and no corresponding changes
to the SIP are required. Thus, we find
that the California SIP revision to optout of the federal program, as approved
in 1999, meets the requirements of CAA
sections 182(c)(4)(A) and 246 for
Ventura for the 2008 ozone NAAQS.
4. Gasoline Vapor Recovery
Section 182(b)(3) of the CAA requires
states to submit a SIP revision by
November 15, 1992, that requires
owners or operators of gasoline
dispensing systems to install and
operate gasoline vehicle refueling vapor
recovery (‘‘Stage II’’) systems in ozone
nonattainment areas classified as
Moderate and above. California’s ozone
nonattainment areas implemented Stage
II vapor recovery well before the passage
of the CAA Amendments of 1990.132
Section 202(a)(6) of the CAA requires
the EPA to promulgate standards
requiring motor vehicles to be equipped
with onboard refueling vapor recovery
(ORVR) systems. The EPA promulgated
the first set of ORVR system regulations
in 1994 for phased implementation on
vehicle manufacturers, and since the
end of 2006, essentially all new
gasoline-powered light- and mediumduty vehicles are ORVR-equipped.133
Section 202(a)(6) also authorizes the
EPA to waive the SIP requirement under
CAA section 182(b)(3) for installation of
Stage II vapor recovery systems after
such time as the EPA determines that
ORVR systems are in widespread use
throughout the motor vehicle fleet.
Effective May 16, 2012, the EPA waived
the requirement of CAA section
182(b)(3) for Stage II vapor recovery
systems in ozone nonattainment areas
regardless of classification.134 Thus, a
SIP submittal meeting CAA section
182(b)(3) is not required for the 2008
ozone NAAQS.
While a SIP submittal meeting CAA
section 182(b)(3) is not required for the
2008 ozone NAAQS, under California
state law (i.e., Health and Safety Code
section 41954), CARB is required to
adopt procedures and performance
standards for controlling gasoline
emissions from gasoline marketing
131 64
FR 46849 (August 27, 1999).
Preamble, 57 FR 13498 at 13514
(April 16, 1992).
133 77 FR 28772, at 28774 (May 16, 2012).
134 See 40 CFR 51.126(b).
132 General
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operations, including transfer and
storage operations. State law also
authorizes CARB, in cooperation with
local air districts, to certify vapor
recovery systems, to identify defective
equipment and to develop test methods.
CARB has adopted numerous revisions
to its vapor recovery program
regulations and continues to rely on its
vapor recovery program to achieve
emissions reductions in ozone
nonattainment areas in California.
In Ventura County, the installation
and operation of CARB-certified vapor
recovery equipment is required and
enforced through VCAPCD Rule 70
(‘‘Storage And Transfer Of Gasoline’’),
which was most recently approved into
the SIP on January 31, 2011.135
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5. Enhanced Ambient Air Monitoring
Section 182(c)(1) of the CAA requires
that all ozone nonattainment areas
classified as Serious or above
implement measures to enhance and
improve monitoring for ambient
concentrations of ozone, NOX, and VOC,
and to improve monitoring of emissions
of NOX and VOC. The enhanced
monitoring network for ozone is referred
to as the photochemical assessment
monitoring station (PAMS) network.
The EPA promulgated final PAMS
regulations on February 12, 1993.136
On November 10, 1993, CARB
submitted to the EPA a SIP revision
addressing the PAMS network for six
ozone nonattainment areas in California,
including Ventura County, to meet the
enhanced monitoring requirements of
CAA section 182(c)(1) and the PAMS
regulations. The EPA determined that
the PAMS SIP revision met all
applicable requirements for enhanced
monitoring and approved the PAMS
submittal into the California SIP.137
Prior to 2006, the EPA’s ambient air
monitoring regulations in 40 CFR part
58 (‘‘Ambient Air Quality
Surveillance’’) set forth specific SIP
requirements (see former 40 CFR 52.20).
In 2006, the EPA significantly revised
and reorganized 40 CFR part 58.138
Under revised 40 CFR part 58, SIP
revisions are no longer required; rather,
compliance with EPA monitoring
regulations is established through
review of required annual monitoring
network plans.139 The 2008 Ozone SRR
135 76 FR 5277 (January 31, 2011). See also, 69 FR
29451 (May 24, 2004) (The EPA’s approval of an
earlier version of VCAPCD Rule 70 as meeting the
requirements of CAA section 182(b)(3)).
136 58 FR 8452 (February 12, 1993).
137 82 FR 45191 (September 28, 2017).
138 71 FR 61236 (October 17, 2006).
139 40 CFR 58.2(b) now provides that, ‘‘The
requirements pertaining to provisions for an air
quality surveillance system in the SIP are contained
in this part.’’
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made no changes to these
requirements.140
The 2016 Ventura County Ozone SIP
does not specifically address the
enhanced ambient air monitoring
requirement in CAA section 182(c)(1).
However, we note that CARB includes
the ambient monitoring network within
Ventura County in its annual
monitoring network plan that is
submitted to the EPA, and that we have
approved the most recent annual
monitoring network plan (‘‘Annual
Network Plan Covering Monitoring
Operations in 25 California Air Districts
(June 2018)’’ or ‘‘2018 ANP’’) with
respect to the Ventura County
element.141 Based on our review and
approval of the 2018 ANP with respect
to Ventura County and our earlier
approval of the PAMS SIP revision, we
propose to find that CARB and VCAPCD
meet the enhanced monitoring
requirements under CAA section
182(c)(1) for Ventura County with
respect to the 2008 ozone NAAQS.
IV. Proposed Action
For the reasons discussed in this
notice, under CAA section 110(k)(3), the
EPA is proposing to approve as a
revision to the California SIP the
following portions of the 2016 Ventura
County Ozone SIP submitted by CARB
on April 11, 2017 and December 5,
2018:
• Base year emissions inventory
element in the 2016 Ventura County
AQMP as meeting the requirements of
CAA sections 172(c)(3) and 182(a)(1)
and 40 CFR 51.1115 for the 2008 ozone
NAAQS;
• Emissions statement element in the
2016 Ventura County AQMP as meeting
the requirements of CAA section
182(a)(3)(B) and 40 CFR 51.1102 for the
2008 ozone NAAQS;
• RACM demonstration element in
the 2016 Ventura County AQMP as
meeting the requirements of CAA
section 172(c)(1) and 40 CFR 51.1112(c)
for the 2008 ozone NAAQS;
• Attainment demonstration element
for the 2008 ozone NAAQS in the 2016
Ventura County AQMP as meeting the
requirements of CAA section
182(c)(2)(A) and 40 CFR 51.1108;
• ROP demonstration element in the
2016 Ventura County AQMP as meeting
the requirements of CAA 182(b)(1) and
140 The 2008 ozone SRR addresses PAMS-related
requirements at 80 FR 12264, at 12291 (March 6,
2015).
141 Letter dated November 26, 2018, from Gwen
Yoshimura, Manager, Air Quality Analysis Office,
EPA Region IX, to Ravi Ramalingam, Chief,
Consumer Products and Air Quality Assessment
Branch, Air Quality Planning and Science Division,
CARB.
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70129
40 CFR 51.1110(a)(2) for the 2008 ozone
NAAQS;
• RFP demonstration element in the
2018 SIP Update, as clarified in August
2019,142 as meeting the requirements of
CAA sections 172(c)(2) and 182(c)(2)(B),
and 40 CFR 51.1110(a)(2)(ii) for the
2008 ozone NAAQS;
• Motor vehicle emissions budgets in
the 2016 Ventura County AQMP for the
RFP milestone/attainment year of 2020
(as shown in Table 5) because they are
consistent with the RFP and attainment
demonstrations for the 2008 ozone
NAAQS proposed for approval herein
and meet the other criteria in 40 CFR
93.118(e); and
• General conformity budgets of VOC
and NOX (as shown in Table 6) for
Naval Base Ventura County, as meeting
the requirements of CAA section 176(c)
and 40 CFR 93.161.
We are also proposing to find that the:
• Enhanced vehicle inspection and
maintenance program in Ventura
County meets the requirements of CAA
section 182(c)(3) and 40 CFR 51.1102 for
the 2008 ozone NAAQS;
• California SIP revision to opt-out of
the federal Clean Fuels Fleet Program
meets the requirements of CAA sections
182(c)(4)(A) and 246 and 40 CFR
51.1102 for the 2008 ozone NAAQS
with respect to Ventura County; and
• Enhanced monitoring in Ventura
County meets the requirements of CAA
section 182(c)(1) and 40 CFR 51.1102 for
the 2008 ozone NAAQS.143
With respect to the motor vehicle
emissions budgets, we are proposing to
limit the duration of the approval of the
budgets to last only until the effective
date of the EPA’s adequacy finding for
any subsequently submitted budgets.
We are doing so at CARB’s request and
in light of the benefits of using
EMFAC2017-derived budgets prior to
our taking final action on the future SIP
revision that includes the updated
budgets.
In addition, we are proposing, under
CAA section 110(k)(4), to approve
conditionally the contingency measure
element of the 2016 Ventura County
Ozone SIP as meeting the requirements
142 Letter dated August 29, 2019, from Dr.
Michael T. Benjamin, Chief, Air Quality Planning
and Science Division, CARB, to Amy Zimpfer,
Assistant Director, Air Division, EPA Region IX.
143 Regarding other applicable requirements for
the 2008 ozone NAAQS in Ventura County, the EPA
has previously approved SIP revisions that address
the nonattainment area requirements for
implementation of RACT for Ventura County for the
2008 ozone NAAQS. See 80 FR 2016 (January 15,
2015) (approval of Ventura County RACT SIP). With
respect to the Nonattainment NSR SIP for Ventura
County for the 2008 ozone NAAQS, the EPA
proposed approval at 84 FR 20604 (May 10, 2019)
and is expected to take final action in the near
future.
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of CAA sections 172(c)(9) and 182(c)(9)
for RFP and attainment contingency
measures. Our proposed approval is
based on commitments by the District
and CARB to supplement the element
through submission, as a SIP revision
(within one year of the effective date of
our final conditional approval action),
of a revised District rule or rules that
would add new limits or other
requirements if an RFP milestone is not
met or if Ventura County fails to attain
the 2008 ozone NAAQS by the
applicable attainment date.144
The EPA is soliciting public
comments on the issues discussed in
this document. We will accept
comments from the public on this
proposal for the next 30 days and will
consider comments before taking final
action.
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V. Statutory and Executive Order
Reviews
Under the Clean Air Act, the
Administrator is required to approve a
SIP submission that complies with the
provisions of the Act and applicable
federal regulations. 42 U.S.C. 7410(k);
40 CFR 52.02(a). Thus, in reviewing SIP
submissions, the EPA’s role is to
approve state choices, provided that
they meet the criteria of the Clean Air
Act. Accordingly, this proposed action
merely proposes to approve, or
conditionally approve, state plans as
meeting federal requirements and does
not impose additional requirements
beyond those imposed by state law. For
that reason, this proposed action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• Is not an Executive Order 13771 (82
FR 9339, February 2, 2017) regulatory
action because SIP approvals are
exempted under Executive Order 12866;
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
144 Letter dated August 16, 2019, from Michael
Villegas, Air Pollution Control Officer, VCAPCD, to
Richard Corey, Executive Officer, CARB; and letter
dated August 30, 2019, from Richard W. Corey,
Executive Officer, CARB, to Mike Stoker, Regional
Administrator, EPA Region IX.
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in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the Clean Air Act;
and
• Does not provide the EPA with the
discretionary authority to address
disproportionate human health or
environmental effects with practical,
appropriate, and legally permissible
methods under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, the SIP is not approved
to apply on any Indian reservation land
or in any other area where the EPA or
an Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, the proposed rule does
not have tribal implications and will not
impose substantial direct costs on tribal
governments or preempt tribal law as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000).
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Nitrogen dioxide, Ozone, Reporting and
recordkeeping requirements, Volatile
organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 5, 2019.
Michael Stoker,
Regional Administrator, Region IX.
[FR Doc. 2019–27545 Filed 12–19–19; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R10–OAR–2019–0669; FRL–10003–
32–Region 10]
Air Plan Approval; Washington;
Wallula Second 10-Year Maintenance
Plan
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
PO 00000
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The Environmental Protection
Agency (EPA) is proposing to approve a
plan for the Wallula area in Washington
State that addresses the second 10-year
maintenance period for particulate
matter with an aerodynamic diameter
less than or equal to a nominal 10
micrometers (PM10). This plan relies
upon the control measures contained in
the first 10-year maintenance plan, with
revisions to reflect updated permits and
agreements, also proposed for approval
in this action. Lastly, we are proposing
to take final agency action on high wind
and wildfire exceptional events
associated with the Wallula area.
DATES: Written comments must be
received on or before January 21, 2020.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R10–
OAR–2019–0669, at https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Once submitted, comments cannot be
edited or removed from Regulations.gov.
The EPA may publish any comment
received to its public docket. Do not
submit electronically any information
you consider to be Confidential
Business Information (CBI) or other
information whose disclosure is
restricted by statute. Multimedia
submissions (audio, video, etc.) must be
accompanied by a written comment.
The written comment is considered the
official comment and should include
discussion of all points you wish to
make. The EPA will generally not
consider comments or comment
contents located outside of the primary
submission (i.e., on the web, cloud, or
other file sharing system). For
additional submission methods, the full
EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www.epa.gov/dockets/
commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT: Jeff
Hunt, EPA Region 10, 1200 Sixth
Avenue—Suite 155, Seattle, WA 98101,
at (206) 553–0256, or hunt.jeff@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, it is
intended to refer to the EPA. This
supplementary information section is
arranged as follows:
SUMMARY:
Table of Contents
I. Background
II. Requirements of a Maintenance Plan
III. Analysis of Washington’s Submission
A. Attainment Emissions Inventory
B. Maintenance Demonstration
C. Monitoring Network
D. Verification of Continued Attainment
E. Contingency Provisions
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Agencies
[Federal Register Volume 84, Number 245 (Friday, December 20, 2019)]
[Proposed Rules]
[Pages 70109-70130]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-27545]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R09-OAR-2018-0146; FRL-10003-39-Region 9]
Approval of Air Quality Implementation Plans; California; Ventura
County; 8-Hour Ozone Nonattainment Area Requirements
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is proposing to
approve, or conditionally approve, all or portions of two state
implementation plan (SIP) revisions submitted by the State of
California to meet Clean Air Act (CAA or ``the Act'') requirements for
the 2008 8-hour ozone national ambient air quality standards (NAAQS or
``standards'') in the Ventura County, California (``Ventura County'')
ozone nonattainment area. The two SIP revisions include the ``Final
2016 Ventura County Air Quality Management Plan,'' and the Ventura
County portion of the ``2018 Updates to the California State
Implementation Plan.'' In today's action, the EPA refers to these
submittals collectively as the ``2016 Ventura County Ozone SIP.'' The
2016 Ventura County Ozone SIP addresses the nonattainment area
requirements for the 2008 ozone NAAQS, including the requirements for
an emissions inventory, attainment demonstration, reasonable further
progress, reasonably available control measures, contingency measures,
among others; and establishes motor vehicle emissions budgets. The EPA
is proposing to approve the 2016 Ventura County Ozone SIP as meeting
all the applicable ozone nonattainment area requirements except for the
contingency measure requirement, for which the EPA is proposing
conditional approval. In addition, the EPA is beginning the adequacy
process for the 2020 motor vehicle emissions budgets in the 2016
Ventura County Air Quality Management Plan through this proposed rule.
DATES: Written comments must arrive on or before January 21, 2020.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R09-
OAR-2018-0146 at https://www.regulations.gov. For comments submitted at
Regulations.gov, follow the online instructions for submitting
comments. Once submitted, comments cannot be edited or removed from
Regulations.gov. The EPA may publish any comment received to its public
docket. Do not submit electronically any information you consider to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Multimedia submissions (audio,
video, etc.) must be accompanied by a written comment. The written
comment is considered the official comment and should include
discussion of all points you wish to make. The EPA will generally not
consider comments or comment contents located outside of the primary
submission (i.e., on the web, cloud, or
[[Page 70110]]
other file sharing system). For additional submission methods, please
contact the person identified in the FOR FURTHER INFORMATION CONTACT
section. For the full EPA public comment policy, information about CBI
or multimedia submissions, and general guidance on making effective
comments, please visit https://www.epa.gov/dockets/commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT: John Kelly, Air Planning Office (AIR-
2), EPA Region IX, 75 Hawthorne Street, San Francisco, CA 94105, (415)
947-4151, or by email at [email protected].
SUPPLEMENTARY INFORMATION: Throughout this document, ``we,'' ``us,''
and ``our'' refer to the EPA.
Table of Contents
I. Regulatory Context
A. Ozone Standards, Area Designations, and SIPs
B. The Ventura County Ozone Nonattainment Area
C. CAA and Regulatory Requirements for 2008 Ozone Nonattainment
Area SIPs
II. Submissions From the State of California To Address 2008 Ozone
Requirements in Ventura County
A. Summary of Submissions
B. CAA Procedural Requirements for Adoption and Submission of
SIP Revisions
III. Evaluation of the 2016 Ventura County Ozone SIP
A. Emissions Inventories
B. Emissions Statement
C. Reasonably Available Control Measures Demonstration
D. Attainment Demonstration
E. Rate of Progress Plan and Reasonable Further Progress
Demonstration
F. Contingency Measures
G. Motor Vehicle Emissions Budgets for Transportation Conformity
H. General Conformity Budgets
I. Other Clean Air Act Requirements Applicable to Serious Ozone
Nonattainment Areas
IV. Proposed Action
V. Statutory and Executive Order Reviews
I. Regulatory Context
A. Ozone Standards, Area Designations, and SIPs
Ground-level ozone pollution is formed from the reaction of
volatile organic compounds (VOC) and oxides of nitrogen
(NOX) in the presence of sunlight.\1\ These two pollutants,
referred to as ozone precursors, are emitted by many types of sources,
including on- and off-road motor vehicles and engines, power plants and
industrial facilities, and smaller area sources such as lawn and garden
equipment and paints.
---------------------------------------------------------------------------
\1\ The State of California refers to reactive organic gases
(ROG) rather than VOC in some of its ozone-related SIP submissions.
As a practical matter, ROG and VOC refer to the same set of chemical
constituents, and for the sake of simplicity, we refer to this set
of gases as VOC in this proposed rule.
---------------------------------------------------------------------------
Scientific evidence indicates that adverse public health effects
occur following exposure to ozone, particularly in children and adults
with lung disease. Breathing air containing ozone can reduce lung
function and inflame airways, which can increase respiratory symptoms
and aggravate asthma or other lung diseases.\2\
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\2\ ``Fact Sheet--2008 Final Revisions to the National Ambient
Air Quality Standards for Ozone,'' dated March 2008.
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Under section 109 of the CAA, the EPA promulgates NAAQS for
pervasive air pollutants, such as ozone. The NAAQS are concentration
levels that, the attainment and maintenance of which, the EPA has
determined to be requisite to protect public health and welfare. In
1979, the EPA established the 1-hour ozone NAAQS of 0.12 parts per
million (ppm) (referred to herein as the ``1-hour ozone NAAQS'').\3\
Section 110 of the CAA requires states to develop and submit SIPs to
implement, maintain, and enforce the NAAQS.
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\3\ 44 FR 8202 (February 8, 1979).
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Under the CAA, as amended in 1977, the EPA designated all areas of
the country as ``nonattainment,'' ``attainment,'' or ``unclassifiable''
with respect to each NAAQS, and in so doing, designated Ventura County
(excluding the Channel Islands) as a nonattainment area for
photochemical oxidant (later ozone).\4\ States with nonattainment areas
are required to submit revisions to their SIPs that include a control
strategy and technical analysis to demonstrate how the area will attain
the NAAQS (referred to as an ``attainment demonstration''), and the EPA
took action on a number of related SIP revisions submitted by the
California Air Resources Board (CARB) in the late 1970s and 1980s for
Ventura County.\5\ Under the 1977 CAA Amendments, nonattainment areas
were to have attained the 1-hour ozone NAAQS no later than 1987. By
1990, however, like many other areas throughout the country, Ventura
County had not yet attained the 1-hour ozone NAAQS, and the CAA was
amended to include new SIP requirements and new attainment deadlines.
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\4\ 43 FR 8962, at 8972 (March 3, 1978). Ventura County lies
within California's South Central Coast Air Basin, which includes
the counties of Santa Barbara and San Luis Obispo in addition to
Ventura County.
\5\ Under California law, CARB is the state agency that is
responsible for the adoption and submission to the EPA of California
SIPs and SIP revisions, and it has broad authority to establish
emissions standards and other requirements for mobile sources. Local
and regional air pollution control districts in California are
responsible for the regulation of stationary sources and are
generally responsible for the development of regional air quality
plans. In Ventura County, the Ventura County Air Pollution Control
District develops and adopts air quality management plans to address
CAA planning requirements applicable to that region. Such plans are
then submitted to CARB for adoption and submittal to the EPA as
revisions to the California SIP.
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Under the CAA Amendments of 1990, Ventura County (excluding the
Channel Islands) was classified as a ``Severe-15'' nonattainment area
for the 1-hour ozone NAAQS based on a 1-hour ozone design value of 0.17
parts per million (ppm).\6\ As a Severe-15 ozone nonattainment area,
Ventura County was required to attain the 1-hour ozone NAAQS no later
than November 15, 2005 and was subject to additional SIP planning
requirements, including a revised attainment demonstration.
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\6\ 56 FR 56694 (November 6, 1991). For the 1-hour ozone NAAQS,
the Channel Islands of Ventura County are part of the
unclassifiable/attainment area comprised by the Channel Islands
portion of the South Central Coast Air Basin. See 56 FR 56694, at
56732 (November 6, 1991).
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In the wake of the classification of Ventura County as a Severe-15
nonattainment area for the 1-hour ozone NAAQS, CARB submitted a number
of SIP revisions for Ventura County that contained an attainment
demonstration for the 1-hour ozone NAAQS and other SIP elements, and
that relied on a combination of mobile source control measures adopted
by CARB and stationary source control measures adopted by the Ventura
County Air Pollution Control District (VCAPCD or ``District''). In
connection with these submittals, the EPA took the following actions:
1994 Air Quality Management Plan for Ventura County and
related State Strategy--The EPA approved the control measures, the 15
percent rate of progress demonstration and attainment demonstration,
among other elements, for the 1-hour ozone NAAQS at 62 FR 1150 (January
8, 1997);
Ventura County 1995 Air Quality Management Plan Revision--
The EPA approved the revised rule adoption and implementation schedule
at 62 FR 1150 (January 8, 1997);
Ventura County 1997 Air Quality Management Plan--The EPA
approved certain commitments to adopt and implement control measures at
63 FR 19659 (April 21, 1998).
As noted previously, Ventura County was required to attain the 1-
hour ozone NAAQS no later than 2005, and in 2009, the EPA determined
that Ventura County had attained the 1-hour ozone NAAQS by the 2005
applicable attainment date.\7\ Since 2005, 1-hour
[[Page 70111]]
ozone design values in Ventura County have decreased from 0.12 ppm in
2005 (based on 2003-2005 data) to 0.10 ppm in 2018 (based on 2016-2018
data) and are consistent with continued attainment of the 1-hour ozone
NAAQS.\8\
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\7\ 74 FR 25153 (May 27, 2009).
\8\ Under EPA regulations at 40 CFR 50.9 and appendix H, the 1-
hour ozone NAAQS is attained at a site when the expected number of
days per calendar year with maximum hourly average concentrations
above 0.12 ppm is equal to or less than 1. The design value for 1-
hour ozone is generally the fourth highest daily maximum 1-hour
ozone concentration measured during a 3-year period at each site in
the area, assuming 3 complete years of data. The highest design
value among the various ozone monitoring sites represents the design
value for the area. The data for Ventura County is from CARB,
Aerometric Data Analysis System Air Quality Database, Ventura County
Ozone Trends Summary Report, September 11, 2019.
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In 1997, the EPA revised the NAAQS for ozone, setting it at 0.08
ppm averaged over an 8-hour timeframe (referred to herein as the ``1997
ozone NAAQS'') to replace the existing 1-hour ozone NAAQS of 0.12
ppm.\9\ In 2004, the EPA designated and classified Ventura County
(excluding the Channel Islands) as a ``Moderate'' nonattainment area
for the 1997 ozone NAAQS but later granted CARB's request to reclassify
Ventura County to ``Serious'' nonattainment for the 1997 ozone
NAAQS.\10\ Serious ozone nonattainment areas were required to attain
the 1997 ozone NAAQS as expeditiously as practicable, but no later than
June 15, 2013. In 2012, the EPA determined that Ventura County attained
the 1997 ozone NAAQS based on the ambient data for years 2009-2011.\11\
Since 2011, the eight-hour ozone design values for Ventura County have
decreased from 0.083 ppm in 2011 (based on 2009-2011 data) to 0.078 ppm
in 2018 (based on 2016-2018 data) and are consistent with continued
attainment of the 1997 ozone NAAQS.\12\
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\9\ 62 FR 38856 (July 18, 1997).
\10\ 69 FR 23857 at 23889 (April 30, 2004); 73 FR 29073 (May 20,
2008).
\11\ 77 FR 56775 (September 14, 2012).
\12\ Under EPA regulations at 40 CFR 50.10 and appendix I, the
1997 ozone NAAQS is attained at a site when the 3-year average of
the annual fourth-highest daily maximum 8-hour average ozone
concentration is less than or equal to 0.08 ppm. This 3-year average
is referred to as the design value. When the design value is less
than or equal to 0.084 ppm (based on the rounding convention in 40
CFR part 50, appendix I) at each monitoring site within the area,
then the area is meeting the 1997 ozone NAAQS. The highest design
value among the various ozone monitoring sites in the area
represents the design value for the area. The data for Ventura
County is from EPA, Design Value Report, dated July 3, 2019.
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In 2008, the EPA lowered the 8-hour ozone NAAQS to 0.075 ppm
(referred to herein as the ``2008 ozone NAAQS'') to replace the 1997
ozone NAAQS of 0.08 ppm.\13\ In 2012, the EPA designated Ventura County
(excluding the Channel Islands) as nonattainment for the 2008 ozone
NAAQS and classified the area as Serious.\14\ Areas classified as
Serious must attain the NAAQS within 9 years of the effective date of
the nonattainment designation.\15\ The SIP revisions that are the
subject of today's proposed action address the Serious nonattainment
area requirements that apply to Ventura County for the 2008 ozone
NAAQS.
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\13\ 73 FR 16436 (March 27, 2008). The EPA further tightened the
8-hour ozone NAAQS to 0.070 ppm in 2015, but this proposed action
relates to the requirements for the 2008 ozone NAAQS. Information on
the 2015 ozone NAAQS is available at 80 FR 65292 (October 26, 2015).
\14\ 77 FR 30088 (May 21, 2012).
\15\ CAA section 181(a)(1), 40 CFR 51.1102 and 51.1103(a).
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B. The Ventura County Ozone Nonattainment Area
The Ventura County nonattainment area for the 2008 ozone NAAQS
consists of the Ventura County portion of California's South Central
Coast Air Basin, excluding the Channel Islands. Ventura County
encompasses approximately 2,200 square miles and has a population of
approximately 874,000 (in 2018); it is located west of Los Angeles
County and is bordered by Kern County to the north, Santa Barbara
County and the Pacific Ocean to the west, and the Pacific Ocean and Los
Angeles County to the south. Ozone in the Ventura County nonattainment
area is caused by both locally generated emissions and transport from
the South Coast Air Basin.\16\ Ocean-going vessels calling on Port
Hueneme or the ports of Los Angeles or Long Beach and transiting
vessels passing through southern California waters, but without calling
at the ports, also impact Ventura County's air quality.
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\16\ The South Coast Air Basin includes Orange County, the
southwestern two-thirds of Los Angeles County, southwestern San
Bernardino County, and western Riverside County.
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C. CAA and Regulatory Requirements for 2008 Ozone Nonattainment Area
SIPs
States must implement the 2008 ozone NAAQS under title I, part D of
the CAA, including sections 171-179B of subpart 1 (``Nonattainment
Areas in General'') and sections 181-185 of subpart 2 (``Additional
Provisions for Ozone Nonattainment Areas''). To assist states in
developing effective plans to address ozone nonattainment problems, in
2015, the EPA issued a SIP Requirements Rule (SRR) for the 2008 ozone
NAAQS (``2008 Ozone SRR'') that addressed implementation of the 2008
standards, including attainment dates, requirements for emissions
inventories, attainment and reasonable further progress (RFP)
demonstrations, among other SIP elements, as well as the transition
from the 1997 ozone NAAQS to the 2008 ozone NAAQS and associated anti-
backsliding requirements.\17\ The 2008 Ozone SRR is codified at 40 CFR
part 51, subpart AA. We discuss the CAA and regulatory requirements for
the elements of 2008 ozone plans relevant to this proposal in more
detail below.
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\17\ 80 FR 12264 (March 6, 2015).
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The EPA's 2008 Ozone SRR was challenged, and on February 16, 2018,
the U.S. Court of Appeals for the D.C. Circuit (``D.C. Circuit'')
published its decision in South Coast Air Quality Management District
v. EPA\18\ (``South Coast II'') \19\ vacating portions of the 2008
Ozone SRR. The only aspect of the South Coast II decision that affects
this proposed action is the vacatur of the alternative baseline year
for RFP plans. More specifically, the 2008 Ozone SRR required states to
develop the baseline emissions inventory for RFP plans using the
emissions for the most recent calendar year for which states submit a
triennial inventory to the EPA under subpart A (``Air Emissions
Reporting Requirements'') of 40 CFR part 51, which was 2011. However,
the 2008 Ozone SRR allowed states to use an alternative year, between
2008 and 2012, for the baseline emissions inventory provided that the
state demonstrated why the alternative baseline year was appropriate.
In the South Coast II decision, the D.C. Circuit vacated the provisions
of the 2008 Ozone SRR that allowed states to use an alternative
baseline year for demonstrating RFP.
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\18\ South Coast Air Quality Management District v. EPA, 882
F.3d 1138 (D.C. Cir. 2018) (``South Coast II'').
\19\ The term ``South Coast II'' is used in reference to the
2018 court decision to distinguish it from a decision published in
2006 also referred to as ``South Coast.'' The earlier decision
involved a challenge to the EPA's Phase 1 implementation rule for
the 1997 ozone NAAQS. South Coast Air Quality Management Dist. v.
EPA, 472 F.3d 882 (D.C. Cir. 2006).
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II. Submissions From the State of California To Address 2008 Ozone
Requirements in Ventura County
A. Summary of Submissions
In this document, we are proposing action on all or portions of two
SIP revisions, which are described in detail in the following
paragraphs. Collectively, we refer to the relevant portions of the two
SIP revisions as the 2016 Ventura County Ozone SIP.
[[Page 70112]]
1. VCAPCD's 2016 Air Quality Management Plan
On April 11, 2017, CARB submitted the Final 2016 Ventura County Air
Quality Management Plan (February 14, 2017) (``2016 Ventura County
AQMP'') to the EPA as a revision to the California SIP.\20\ The 2016
Ventura County AQMP addresses the nonattainment area requirements for
Ventura County for the 2008 ozone NAAQS.
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\20\ Letter dated April 11, 2017, from Richard W. Corey,
Executive Officer, CARB, to Alexis Strauss, Acting Regional
Administrator, EPA Region IX.
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More specifically, the 2016 Ventura County AQMP includes a base
year emissions inventory,\21\ reasonably available control measure
(RACM) demonstration, RFP demonstration, attainment demonstration,
contingency measures, motor vehicle and general conformity emissions
budgets, and it also addresses the emissions statement requirement. The
appendices to the 2016 Ventura County AQMP provide documentation for
the emissions inventories, RACM demonstration, and the photochemical
modeling conducted in support of the attainment demonstration. Further
support for the attainment demonstration is provided in Appendix J
(``Ventura County Unmonitored Area Analysis'') and Appendix K
(``Ventura County Weight of Evidence Assessment''). The April 11, 2017
SIP submittal of the 2016 Ventura County AQMP was accompanied by public
process documentation at both the County and State levels.
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\21\ The 2012 base year emissions inventory included in the 2016
Ventura County AQMP supersedes and replaces a previous submittal of
the 2012 base year emissions inventory for Ventura County in the
``8-Hour Ozone State Implementation Plan Emission Inventory
Submittal'' (the ``Multi-Area Emission Inventory''). The Multi-Area
Emission Inventory was submitted by CARB on July 17, 2014, and
included 2012 base year emissions inventories for 16 nonattainment
areas, including Ventura County. Relative to the corresponding
inventory for Ventura County in the Multi-Area Emission Inventory,
the 2012 base year emissions inventory in the 2016 Ventura County
AQMP reflects updated stationary, area, and nonroad source
calculations as well as an updated version of the EMFAC model for
on-road motor vehicle estimates. In a letter dated November 15,
2019, CARB withdrew the earlier submitted 2012 base year emissions
inventory for Ventura County in light of the updated inventory in
the 2016 Ventura County AQMP. Letter dated November 15, 2019, from
Richard W. Corey, Executive Officer, CARB, to Mike Stoker, Regional
Administrator, EPA Region IX. In section III.A of this document, we
are proposing approval of the superseding 2012 base year emissions
inventory in the 2016 Ventura County AQMP.
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Since submittal of the 2016 Ventura County AQMP, CARB has replaced
or supplemented certain elements of the 2016 Ventura County AQMP (such
as the RFP demonstration and contingency measure element) through a SIP
revision submittal dated December 5, 2018 and discussed in more detail
in the following subsection. In addition, by letter dated August 29,
2019, CARB has provided some additional information related to the
motor vehicle emissions budgets in the 2016 Ventura County AQMP.\22\
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\22\ Letter dated August 29, 2019, from Dr. Michael T. Benjamin,
Chief, Air Quality Planning and Science Division, CARB, to Amy
Zimpfer, Assistant Director, Air Division, EPA Region IX, including
attachments A and B.
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2. CARB's 2018 Updates to the California State Implementation Plan
On December 5, 2018, CARB submitted the 2018 Updates to the
California State Implementation Plan (``2018 SIP Update'') to the EPA
as a revision to the California SIP.\23\ CARB adopted the 2018 SIP
Update on October 25, 2018. CARB developed the 2018 SIP Update in
response to the court's decision in South Coast II vacating the 2008
Ozone SRR with respect to the use of an alternate baseline year for
demonstrating RFP and to provide additional information pertaining to
the contingency measure requirement in the wake of the court decision
in Bahr v. EPA.\24\ The 2018 SIP Update includes an RFP demonstration
using the required 2011 baseline year for Ventura County for the 2008
ozone NAAQS. The RFP demonstration in the 2018 SIP Update for Ventura
County supersedes and replaces the RFP demonstration in the 2016
Ventura County AQMP.\25\
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\23\ Letter dated December 5, 2018, from Richard Corey,
Executive Officer, CARB, to Mike Stoker, Regional Administrator, EPA
Region IX.
\24\ Bahr v. EPA, 836 F.3d 1218 (9th Cir. 2016) (``Bahr v.
EPA''). In Bahr v. EPA, the court rejected the EPA's longstanding
interpretation of CAA section 172(c)(9) as allowing for early
implementation of contingency measures. The court concluded that a
contingency measure must take effect at the time the area fails to
make RFP or attain by the applicable attainment date, not before.
\25\ CARB withdrew the RFP demonstration from the 2016 Ventura
County AQMP in light of the revised RFP demonstration for Ventura
County in the 2018 SIP Update. Letter dated November 15, 2019, from
Richard W. Corey, Executive Officer, CARB, to Mike Stoker, Regional
Administrator, EPA Region IX. In section III.E of this document, we
are proposing approval of the superseding RFP demonstration for
Ventura County in the 2018 SIP Update.
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The 2018 SIP Update includes updates for 8 different California
ozone nonattainment areas. We have already taken action to approve the
San Joaquin Valley and South Coast portions of the 2018 SIP Update.\26\
In today's document, we are proposing action on the Ventura County
portion of the 2018 SIP Update. Also, to supplement the contingency
measure element of the 2016 Ventura County Ozone SIP, in a letter dated
August 30, 2019, CARB forwarded to the EPA an August 16, 2019 letter of
commitment from the District.\27\ In its letter, the District commits
to modify at least one of three existing rules to create a contingency
measure that will be triggered if the area fails to meet an RFP
milestone or to attain the 2008 ozone NAAQS and to transmit the rule,
as amended, to CARB for submittal to the EPA.\28\ In the August 30,
2019 letter, CARB commits to submit the revised District rule or rules
to the EPA as a SIP revision within 12 months of the effective date of
the EPA's final conditional approval of the contingency measure element
of the 2016 Ventura County Ozone SIP.
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\26\ 84 FR 11198 (March 25, 2019) (final approval of the San
Joaquin Valley portion of the 2018 SIP Update) and 84 FR 52005
(October 1, 2019) (final approval of the South Coast portion of the
2018 SIP Update).
\27\ Letter dated August 30, 2019, from Richard Corey, Executive
Officer, CARB, to Mike Stoker, Regional Administrator, EPA Region
IX.
\28\ Letter dated August 16, 2019, from Michael Villegas, VCAPCD
Air Pollution Control Officer, to Richard Corey, CARB Executive
Officer, provided as enclosure to August 30, 2019 CARB letter.
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B. CAA Procedural Requirements for Adoption and Submission of SIP
Revisions
Sections 110(a) and 110(l) of the CAA require a state to provide
reasonable public notice and opportunity for public hearing prior to
the adoption and submission of a SIP or SIP revision. To meet this
requirement, every SIP submittal should include evidence that adequate
public notice was given and an opportunity for a public hearing was
provided consistent with the EPA's implementing regulations in 40 CFR
51.102.
Both the District and CARB have satisfied the applicable statutory
and regulatory requirements for reasonable public notice and hearing
prior to the adoption and submittal of the SIP revisions that comprise
the 2016 Ventura County Ozone SIP. With respect to the 2016 Ventura
County AQMP, the District provided two public review periods: One for
the initial draft 2016 Ventura County AQMP and a second for the final
draft 2016 Ventura County AQMP. Combined, the public review periods
lasted 43 days. The District published notices of the two public review
periods on its website and in a local newspaper. The District also
published notice of a public hearing to be held on February 14, 2017,
for the adoption of the 2016 Ventura County AQMP. On February 14, 2017,
the District held the public hearing, and, through a minute order,
adopted the 2016 Ventura County AQMP and
[[Page 70113]]
directed staff to forward the plan to CARB for inclusion in the
California SIP.
CARB also provided public notice and opportunity for public comment
on the 2016 Ventura County AQMP. On February 17, 2017, CARB released
for public review its Staff Report for the 2016 Ventura County AQMP and
published a notice of public meeting to be held on March 23, 2017, to
consider adoption of the 2016 Ventura County AQMP.\29\ On March 23,
2017, CARB held the hearing and adopted the 2016 Ventura County AQMP as
a revision to the California SIP, and directed the Executive Officer to
submit the 2016 Ventura County AQMP to the EPA for approval into the
California SIP.\30\ On April 11, 2017, the Executive Officer of CARB
submitted the 2016 Ventura County AQMP to the EPA and included a public
comments log entry indicating that there were no public comments during
the Board hearing held on March 23, 2017.\31\
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\29\ Notice of Public Meeting to Consider the 2016 Ozone SIP for
Ventura County, signed by Richard Corey, Executive Officer, CARB,
February 17, 2017.
\30\ CARB Resolution 17-5.
\31\ CARB ``Public Comment Log,'' dated March 30, 2017. See
also, Transcript of the March 23, 2017 Meeting of the State of
California Air Resources Board, 7-8.
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With respect to the 2018 SIP Update, CARB also provided public
notice and opportunity for public comment. On September 21, 2018, CARB
released for public review the 2018 SIP Update and published a notice
of public meeting to be held on October 23, 2018, to consider adoption
of the 2018 SIP Update.\32\ On October 23, 2018, through Resolution 18-
50, CARB adopted the 2018 SIP Update. On December 5, 2018, CARB
submitted the 2018 SIP Update to the EPA.
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\32\ Notice of Public Meeting to Consider the 2018 Updates to
the California State Implementation Plan signed by Richard Corey,
Executive Officer, CARB, September 21, 2018.
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Based on information provided in each of the SIP revisions
summarized above, the EPA has determined that all hearings were
properly noticed. Therefore, we find that the submittals of the 2016
Ventura County AQMP and the 2018 SIP Update meet the procedural
requirements for public notice and hearing in CAA sections 110(a) and
110(l) and 40 CFR 51.102.
III. Evaluation of the 2016 Ventura County Ozone SIP
A. Emissions Inventories
1. Statutory and Regulatory Requirements
CAA sections 172(c)(3) and 182(a)(1) require states to submit for
each ozone nonattainment area a ``base year inventory'' that is a
comprehensive, accurate, current inventory of actual emissions from all
sources of the relevant pollutant or pollutants in the area. In
addition, the 2008 Ozone SRR requires that the inventory year be
selected consistent with the baseline year for the RFP demonstration,
which is the most recent calendar year for which a complete triennial
inventory is required to be submitted to the EPA under the Air
Emissions Reporting Requirements.\33\
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\33\ 2008 Ozone SRR at 40 CFR 51.1115(a) and the Air Emissions
Reporting Requirements at 40 CFR part 51, subpart A.
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The EPA has issued guidance on the development of base year and
future year emissions inventories for ozone and other pollutants.\34\
Emissions inventories for ozone must include emissions of VOC and
NOX and represent emissions for a typical ozone season
weekday.\35\ States should include documentation explaining how the
emissions data were calculated. In estimating mobile source emissions,
states should use the latest emissions models and planning assumptions
available at the time the SIP is developed.\36\
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\34\ ``Emissions Inventory Guidance for Implementation of Ozone
and Particulate Matter National Ambient Air Quality Standards
(NAAQS) and Regional Haze Regulations,'' EPA-454/B-17-002, May 2017.
At the time the 2016 Ventura County AQMP was developed, the
following EPA emissions inventory guidance applied: ``Emissions
Inventory Guidance for Implementation of Ozone and Particulate
Matter National Ambient Air Quality Standards (NAAQS) and Regional
Haze Regulations,'' EPA-454-R-05-001, August 2005.
\35\ 40 CFR 51.1115(a) and (c), and 40 CFR 51.1100(bb) and (cc).
\36\ 80 FR 12264, at 12290 (March 6, 2015).
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Future baseline emissions inventories must reflect the most recent
population, employment, travel and congestion projections for the area.
In this context, future ``baseline'' emissions inventories refer to
emissions estimates for a given year and area that reflect rules and
regulations and other measures that are already adopted and that take
into account expected growth. Future baseline emissions inventories are
necessary to show the projected effectiveness of SIP control measures.
Both the base year and future year inventories are necessary for
photochemical modeling to demonstrate attainment.
2. Summary of State's Submission
The 2016 Ventura County AQMP includes base year (2012) and future
year baseline inventories for NOX and VOC for the Ventura
County ozone nonattainment area. Documentation for the inventories is
found in Chapter 2 (``2012 Baseline Emissions Inventory'') and Appendix
A (``Ventura County Emissions Inventory Documentation'') of the 2016
Ventura County AQMP. Because ozone levels in Ventura County are
typically higher from May through October, these inventories represent
average summer day emissions. The 2012 base year and future year
inventories in the 2016 Ventura County AQMP reflect District rules
adopted prior to July 2015, and CARB rules adopted by November
2015.\37\ The mobile source portions of both base year and projected
future year inventories were developed using California's EPA-approved
mobile source emissions model, EMFAC2014, for estimating on-road motor
vehicle emissions.\38\
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\37\ The 2012 base year and future year baseline emissions
inventories in the 2016 Ventura County AQMP exclude non-
anthropogenic ``natural sources'' emissions such as biogenics,
geogenics, and wildfires. However, emissions from such natural
sources are included in the emissions inventories used for the
attainment demonstration because they affect ozone formation.
\38\ EMFAC is short for EMission FACtor.
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Emissions estimates of VOC and NOX in the 2016 Ventura
County AQMP are grouped into two general categories: (1) Stationary and
area-wide sources, and (2) mobile sources, which are comprised of on-
road motor vehicles and other mobile (off-road) sources. Stationary
sources refer to larger ``point'' sources that have a fixed geographic
location, such as power plants, industrial engines, and oil storage
tanks, and that are subject to District permits. Area-wide sources are
emissions sources occuring over a wide geographic area such as consumer
products and architectural coatings. The emissions inventories for the
2016 Ventura County AQMP account for smaller permitted stationary
sources in the area source categories. The mobile sources category is
divided into two major subcategories, ``on-road'' and ``off-road''
mobile sources. On-road mobile sources include light-duty automobiles,
light-, medium-, and heavy-duty trucks, and motorcycles. Off-road
mobile sources include aircraft and boats.
For the 2016 Ventura County AQMP, point source emissions for the
2012 base year emissions inventory are based on reported data from
facilities using the District's annual emissions reporting program,
which applies under District Rule 24 (``Source Recordkeeping, Reporting
and Emissions Statements'') to all stationary sources in Ventura County
that emit more than 25 tons per year (tpy) or more of VOC or
NOX. Area sources include smaller emissions sources
distributed across the nonattainment area. CARB and the
[[Page 70114]]
District estimate emissions for area sources using established
inventory methods, including publicly available emission factors and
activity information. Area source methodologies are described in
Appendix A of the 2016 Ventura County AQMP. To improve and update the
emissions inventory, District staff evaluate the data and methods used
on an annual basis. CARB and District staff coordinate the update
process through the State's Emissions Inventory Technical Advisory
Committee.
On-road emissions inventories in the 2016 Ventura County AQMP are
calculated using CARB's EMFAC2014 model \39\ and the travel activity
data provided by the Southern California Association of Governments
(SCAG) in ``The 2016-2040 Regional Transportation Plan/Sustainable
Communities Strategy.'' \40\ CARB provided emissions inventories for
off-road equipment, including construction and mining equipment,
industrial and commercial equipment, lawn and garden equipment,
agricultural equipment, ocean-going vessels, commercial harbor craft,
locomotives, cargo handling equipment, pleasure craft, and recreational
vehicles. CARB uses several models to estimate emissions for more than
one hundred off-road equipment categories.\41\ The District estimates
aircraft emissions based on information provided by the airport
operators in Ventura County.
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\39\ In December 2015, the EPA approved EMFAC2014 for SIP
development and transportation conformity purposes in California. 80
FR 77337 (December 14, 2015). EMFAC2014 was the most recently
approved version of the EMFAC model that was available at the time
of preparation of the 2016 Ventura County AQMP. Recently, the EPA
approved an updated version of the EMFAC model, EMFAC2017, for
future SIP development and transportation purposes in California. 84
FR 41717 (August 15, 2019).
\40\ See https://scagrtpscs.net/Pages/FINAL2016RTPSCS.aspx.
\41\ 2016 Ventura County AQMP, 22.
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The 2016 Ventura County AQMP distinguishes between emission sources
within Ventura County, which includes coastal emissions (including
marine vessel emissions) within three miles of the coastline, and
emissions sources operating outside the county but within 100 nautical
miles of the coastline. The latter are included in the Outer
Continental Shelf (OCS) category. The base year emissions inventory
reflects only those emissions sources that operate within the
nonattainment area (i.e., within the three miles of the coastline), but
OCS emissions sources affect ozone concentrations in the nonattainment
area and thus are included in the emissions inventories used for the
attainment demonstration in the 2016 Ventura County AQMP.
Future emissions forecasts in the 2016 Ventura County AQMP are
primarily based on demographic and economic growth projections provided
by SCAG (i.e., the metropolitan planning organization (MPO) for Ventura
County), and control factors developed by the District in reference to
the 2012 base year. Growth factors used to project these baseline
inventories are derived mainly from data obtained from SCAG.\42\
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\42\ 2016 Ventura County AQMP, Appendix A, tables A-4 and A-6.
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Under EPA's SIP regulations for nonattainment new source review
(NSR) programs, a state may allow new major stationary sources or major
modifications to use emission reductions credits (ERCs) that were
generated through shutdown or curtailed emissions units occuring before
the base year of an attainment plan. However, to use such ERCs, the
projected emissions inventory used to develop the attainment
demonstration must explicitly include the emissions from such
previously shutdown or curtailed emissions units.\43\ The District has
elected to provide for use of pre-base year ERCs as offsets by
explicitly including such ERCs in the 2020 attainment year inventory.
The ERC set-aside in the attainment year (2020) amounts to 1.72 tons
per day (tpd) of VOC and 0.82 tpd of NOX.
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\43\ 40 CFR 51.165(a)(3)(ii)(C)(1).
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Table 1 provides a summary of the District's 2012 base year and
future attainment year baseline emissions estimates in tpd (average
summer day) for VOC and NOX. These inventories provide the
basis for the control measure analysis and the attainment demonstration
in the 2016 Ventura County AQMP. Based on the inventory for 2012,
stationary, area and mobile sources contribute roughly equally to
county-wide VOC emissions, whereas mobile sources are the predominant
sources of NOX emissions. The inventory for 2012 also shows
the extent (about 40 percent) to which OCS sources contribute to the
overall anthropogenic NOX emissions total used for
attainment modeling purposes.
Table 1--Ventura County 2012 Base Year and 2020 Attainment Year
Emissions Inventories
[Summer planning inventory, tpd]
------------------------------------------------------------------------
2012 2020
Category -------------------------------------------
VOC NOX VOC NOX
------------------------------------------------------------------------
Stationary.................. 8.55 2.08 8.67 1.87
Area Sources................ 11.57 0.95 10.91 0.62
On-Road Mobile Sources...... 8.54 12.62 4.21 6.01
Other (Off-Road) Mobile 8.14 8.78 6.63 7.25
Sources....................
ERCs........................ ......... ......... 1.72 0.82
-------------------------------------------
Total for Ventura County 36.81 24.44 32.14 16.57
Nonattainment Area.....
OCS Sources................. 0.96 16.11 1.37 15.49
-------------------------------------------
Total Anthropogenic 37.76 40.55 33.50 32.06
Emissions Used for
Attainment
Demonstration..........
------------------------------------------------------------------------
Source: 2016 Ventura County AQMP, Appendix A, tables A-7 and A-8. The
sum of the emissions values may not equal the total shown due to
rounding of the numbers.
Following the South Coast II decision, CARB submitted the 2018 SIP
Update to the EPA to, among other things, revise the RFP demonstration
in the 2016 Ventura County AQMP based on a 2011 RFP baseline year
(i.e., rather than 2012).\44\ Our analysis of the emissions inventories
for the 2011 RFP baseline year and RFP milestone years 2017 and 2020
can be found in section III.E below.
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\44\ See 2018 SIP Update, Section III (``SIP Elements for
Ventura County''), 15-20; and Appendix A, pp. A-7--A-10.
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[[Page 70115]]
3. The EPA's Review of the State's Submission
We have reviewed the 2012 base year emissions inventory in the 2016
Ventura County AQMP and the inventory methodologies used by the
District and CARB for consistency with CAA requirements and EPA
guidance. First, as required by EPA regulation, we find that the 2012
inventory includes estimates for VOC and NOX for a typical
ozone season weekday, and that CARB has provided adequate documentation
explaining how the emissions are calculated. Second, we find that the
2012 base year emissions inventory in the 2016 Ventura County AQMP
reflects appropriate emissions models and methodologies, and,
therefore, represents a comprehensive, accurate, and current inventory
of actual emissions during that year in the Ventura County
nonattainment area. Third, we find that selection of year 2012 for the
base year emissions inventory is appropriate because it is consistent
with the 2011 RFP baseline year (from the 2018 SIP Update) because both
inventories are derived from a common set of models and methods.
Therefore, the EPA is proposing to approve the 2012 emissions inventory
in the 2016 Ventura County AQMP as meeting the requirements for a base
year inventory set forth in CAA section 182(a)(1) and 40 CFR 51.1115.
In addition, although the requirement for a base year emissions
inventory applies to the nonattainment area, we find that the
District's estimates of OCS emissions out to 100 nautical miles (i.e.,
beyond the nonattainment area boundary that extends 3 miles offshore)
are reasonable and appropriate to include in the 2016 Ventura County
AQMP given that such emissions must be accounted for in the ozone
attainment demonstration for this nonattainment area.
With respect to future year baseline projections, we have reviewed
the growth and control factors and find them acceptable and conclude
that the future baseline emissions projections in the 2016 Ventura
County AQMP reflect appropriate calculation methods and the latest
planning assumptions.
Furthermore, we note that the future year baseline projections take
into account emissions reductions from adopted State and local rules
and regulations. As a general matter, the EPA will approve a SIP
revision that takes emissions reduction credit for such control
measures only where the EPA has approved the control measures as part
of the SIP. Table 1 in the EPA's memorandum dated September 11, 2019,
to the docket for this rulemaking lists District VOC and NOX
rules that the 2016 Ventura County AQMP relied upon in developing
future year baseline emissions projections. Table 1 also includes
information on EPA approval of these rules and shows that emissions
reductions for stationary sources assumed by the 2016 Ventura County
AQMP for future years are supported by rules approved as part of the
SIP.\45\ With respect to mobile sources, the EPA has taken action in
recent years to approve CARB mobile source regulations into the
California SIP.\46\ We therefore find that the future year baseline
projections in the 2016 Ventura County AQMP are properly supported by
SIP-approved stationary and mobile source control measures.
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\45\ The list of rules in Table 1 of our September 11, 2019
memorandum includes all the District rules for which specific future
year emissions reductions are assumed as shown in Table 3-1 of the
2016 Ventura County AQMP.
\46\ See 81 FR 39424 (June 16, 2016), 82 FR 14446 (March 21,
2017), and 83 FR 23232 (May 18, 2018).
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B. Emissions Statement
1. Statutory and Regulatory Requirements
Section 182(a)(3)(B)(i) of the Act requires states to submit a SIP
revision requiring owners or operators of stationary sources of VOC or
NOX to provide the state with statements of actual emissions
from such sources. Statements must be submitted at least every year and
must contain a certification that the information contained in the
statement is accurate to the best knowledge of the individual
certifying the statement. Section 182(a)(3)(B)(ii) of the Act allows
states to waive the emissions statement requirement for any class or
category of stationary sources that emit less than 25 tpy of VOC or
NOX, if the state provides an inventory of emissions from
such class or category of sources as part of the base year or periodic
inventories required under CAA sections 182(a)(1) and 182(a)(3)(A),
based on the use of emission factors established by the EPA or other
methods acceptable to the EPA.
The 2008 Ozone SRR provides that nonattainment areas are subject to
the requirements of subpart 2 of part D of title I of the CAA that
apply for that area's classification.\47\ For all areas classified
under subpart 2, the emissions statement requirement under CAA section
182(a)(3)(B)(i) applies. The preamble of the 2008 Ozone SRR states that
if an area has a previously approved emissions statement rule for the
1997 ozone NAAQS or the 1-hour ozone NAAQS that covers all portions of
the nonattainment area for the 2008 ozone NAAQS, such rule should be
sufficient for purposes of the emissions statement requirement for the
2008 ozone NAAQS.\48\ The state should review the existing rule to
ensure it is adequate and, if so, may rely on it to meet the emissions
statement requirement for the 2008 ozone NAAQS. Where an existing SIP-
approved emissions statement rule is adequate to meet the requirements
of the 2008 Ozone SRR, states can provide the rationale for that
determination to the EPA in a written statement in their SIP submittal
for the 2008 ozone NAAQS to meet this requirement. States should
identify the various requirements and how each is met by the existing
SIP-approved emissions statement program. Where an emissions statement
requirement is modified for any reason, the state must provide the
revision to the emissions statement rule as part of its SIP.
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\47\ 40 CFR 51.1102.
\48\ See 80 FR 12264, at 12291 (March 6, 2015).
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2. Summary of the State's Submission
The 2016 Ventura County AQMP addresses compliance with the
emissions statement requirement in CAA section 182(a)(3)(B) for the
2008 ozone NAAQS by reference to District Rule 24 (``Source
Recordkeeping, Reporting and Emissions Statements'').\49\ District Rule
24 requires, among other things, emissions reporting from all Ventura
County stationary sources of NOX and VOC, but provides for
waiver of the requirement by the Air Pollution Control Officer for
sources that emit less than 25 tpy.\50\ The EPA approved District Rule
24 as a revision to the Ventura County portion of the California SIP in
2000.\51\ The District determined in the 2016 Ventura County AQMP that
the existing provisions of District Rule 24 meet the emissions
statement requirements for the 2008 ozone NAAQS.\52\
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\49\ 2016 Ventura County AQMP, 16-18.
\50\ District Rule 24 refers to ``reactive organic compounds,''
another term for ``volatile organic compounds.''
\51\ 65 FR 76567 (December 7, 2000).
\52\ 2016 Ventura County AQMP, 17.
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3. The EPA's Review of the State's Submission
For this action, we have reviewed VCAPCD's evaluation of SIP-
approved District Rule 24 for compliance with the specific requirements
for emissions statements under CAA section 182(a)(3)(B). We agree with
the District that District Rule 24 applies within the entire ozone
nonattainment area and that the nonattainment area is the same for both
the 1-hour and 2008 ozone NAAQS; applies to all stationary sources of
VOC and NOX, except those
[[Page 70116]]
emitting less than 25 tpy for which the District has waived the
requirement (consistent with CAA section 182(a)(3)(B)(ii)); and
requires reporting, on an annual basis, of total emissions of VOC and
NOX. Also, as required under CAA section 182(a)(3)(B), we
note that District Rule 24 requires certification that the information
provided to the District is accurate to the best knowledge of the
individual certifying the emissions data.
Therefore, we propose to approve the emissions statement element of
the 2016 Ventura County AQMP as meeting the requirements of CAA section
182(a)(3)(B) and the 40 CFR 51.1102.
C. Reasonably Available Control Measures Demonstration
1. Statutory and Regulatory Requirements
CAA section 172(c)(1) requires that each attainment plan provide
for the implementation of all RACM as expeditiously as practicable
(including such reductions in emissions from existing sources in the
area as may be obtained through implementation of reasonably available
control technology), and also provide for attainment of the NAAQS. The
2008 Ozone SRR requires that, for each nonattainment area required to
submit an attainment demonstration, the state concurrently submit a SIP
revision demonstrating that it has adopted all RACM necessary to
demonstrate attainment as expeditiously as practicable and to meet any
RFP requirements.\53\
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\53\ 40 CFR 51.1112(c).
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The EPA has previously provided guidance interpreting the RACM
requirement in the General Preamble for the Implementation of the Clean
Air Act Amendments of 1990 (``General Preamble'') and in a memorandum
titled ``Guidance on the Reasonably Available Control Measure
Requirement and Attainment Demonstration Submissions for Ozone
Nonattainment Areas.'' \54\ In short, to address the requirement to
adopt all RACM, states should consider all potentially reasonable
control measures for source categories in the nonattainment area to
determine whether they are reasonably available for implementation in
that area and whether they would, if implemented individually or
collectively, advance the area's attainment date by one year or
more.\55\ Any measures that are necessary to meet these requirements
that are not already either federally promulgated, or part of the
state's SIP, must be submitted in enforceable form as part of the
state's attainment plan for the area.\56\
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\54\ See General Preamble, 57 FR 13498 at 13560 (April 16, 1992)
and memorandum dated November 30, 1999, from John S. Seitz,
Director, EPA Office of Air Quality Planning and Standards (OAQPS),
to Regional Air Division Directors, titled ``Guidance on the
Reasonably Available Control Measures (RACM) Requirement and
Attainment Demonstration Submissions for Ozone Nonattainment
Areas.''
\55\ Id. See also 44 FR 20372 (April 4, 1979), and memorandum
dated December 14, 2000, from John S. Seitz, Director, EPA OAQPS, to
Regional Air Division Directors (Regions I, II, III, V and VI),
titled ``Additional Submission on RACM from States with Severe 1-
hour Ozone Nonattainment Area SIPs.''
\56\ For ozone nonattainment areas classified as Moderate or
above, CAA section 182(b)(2) also requires implementation of
reasonably available control technology (RACT) for all major sources
of VOC and for each VOC source category for which the EPA has issued
a control techniques guideline. CAA section 182(f) requires that
RACT under section 182(b)(2) also apply to major stationary sources
of NOX. In Serious areas, a major source is a stationary
source that emits or has the potential to emit at least 50 tpy of
VOC or NOX (see CAA section 182(c) and (f)). Under the
2008 Ozone SRR, states were required to submit SIP revisions meeting
the RACT requirements of CAA sections 182(b)(2) and 182(f) no later
than 24 months after the effective date of designation for the 2008
Ozone NAAQS and to implement the required RACT measures as
expeditiously as practicable but no later than January 1 of the 5th
year after the effective date of designation (see 40 CFR
51.1112(a)). California submitted the CAA section 182 RACT SIP for
Ventura County on July 18, 2014, and the EPA fully approved this
submission at 80 FR 2016 (January 15, 2015).
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2. Summary of the State's Submission
For the 2016 Ventura County AQMP, the District, the Ventura County
Transportation Commission (VCTC) and CARB each undertook a process to
identify and evaluate potential RACM that could contribute to
expeditious attainment of the 2008 ozone NAAQS in Ventura County. We
describe these efforts in the three sections below. To determine what
RACM may be necessary, the District compares, in the 2016 Ventura
County AQMP, the projected 2019 emissions inventory to the 2020
attainment year. Comparing the levels of VOC and NOX in
these two years, during which emissions are declining, allows a simple
subtraction to determine what amount of emissions reductions would
result in 2020 attainment year-level emissions in the year 2019. Since
levels of VOC are identical in both 2019 and 2020, no reduction was
necessary to achieve the attainment year VOC emissions level. However,
for NOX the difference was 2 tpd, so the RACM analyses of
the 2016 Ventura County AQMP appendices E, F and G focus on determining
whether one or more control measures would be potentially reasonable
and would result in a 2 tpd reduction of NOX emissions prior
to the 2020 attainment year.
a. District's RACM Analysis
The District's portion of the RACM demonstration for the 2008 ozone
NAAQS focuses on stationary source controls and is described in the
2016 Ventura County AQMP on pages 54 and 55, and in Appendix E
(``Ventura County Stationary Source Reasonably Available Control
Measure Assessment''). Appendix E contains analyses of all potential
stationary source control measures in the District's jurisdiction.
As background, the District notes that Ventura County was
nonattainment for all prior ozone NAAQS, therefore the District's RACM
analysis builds upon a foundation of District rules developed for
earlier ozone plans. We provide a list of the District's NOX
and VOC rules approved into the California SIP in Table 1 of our
September 11, 2019 memorandum to the docket for this proposed
action.\57\ The 48 SIP-approved District VOC or NOX rules
listed in Table 1 of our September 11, 2019 memorandum establish
emission limits or other types of emissions controls for a wide range
of sources, including use of solvents, refineries, gasoline storage,
architectural coatings, oilfield drilling operations, various types of
commercial coatings, boilers, steam generators and process heaters,
marine coating operations, dry cleaning, and others. These rules have
already provided significant and ongoing reductions toward attainment
of the 2008 ozone NAAQS by 2020. In describing its stationary source
controls, the District also notes the EPA's 2015 approval of its
reasonably available control technology (RACT) SIP and our finding in
that action that District rules that apply to ozone precursor emissions
fulfill RACT requirements for the 2008 ozone NAAQS.\58\
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\57\ Memorandum dated September 11, 2019, from John J. Kelly,
Air Planning Office, EPA Region 9 to ``Approval of Air Quality
Implementation Plans; California; Ventura County; 8-Hour Ozone
Nonattainment Area Requirements; Docket ID EPA-R09-OAR-2018-0146,''
subject: District Rules Assumed for Purposes of Developing Baseline
Emissions Projections.
\58\ 80 FR 2016, January 15, 2015.
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For the stationary source RACM demonstration, the District
evaluated the VOC and NOX rules that were not fully
addressed in the District's 2014 RACT SIP for potential RACM emissions
reductions. The District compared that subset of District rules to
analogous rules adopted by other air districts having nonattainment
areas with higher ozone nonattainment classifications (i.e., South
Coast and San Joaquin Valley, which are both ``Extreme'' nonattainment
areas for the
[[Page 70117]]
2008 ozone NAAQS), as well as certain other air districts such as the
Bay Area Air Quality Management District, to evaluate whether control
technologies available and cost-effective within other areas would be
available and cost-effective for use in Ventura County. The District
also identified a few rules from other air districts that apply to
unregulated source categories in Ventura County. Tables E-2 and E-3 in
Appendix E of the 2016 Ventura County AQMP list the rules that the
District evaluated for the RACM demonstration. Table E-2 includes 13
rules that the District has previously adopted that were compared to
rules in other areas. Table E-3 includes five source categories the
District evaluated, where there is no corresponding rule for that
source category in Ventura County.
The District provides an evaluation of the controls it reviewed for
RACM purposes in Appendix E of the 2016 Ventura County AQMP. The
evaluation includes the following: Description of the Ventura County
sources within the category or sources that would be subject to the
rule; potential NOX and VOC emissions reductions expected
from implementing the rule in Ventura County for the source category
affected by the rule; discussion of the current requirements of the
rule; and discussion of potential additional control measures. This
includes comparison of each District rule to analogous control measures
adopted by other agencies.
Among the 13 existing District NOX or VOC rules that the
District compared to rules in other areas, the District found that
eight of the VCAPCD rule emission limits were as stringent as those
found in analogous rules adopted by the other districts or were not
applicable for the purposes of comparison. The District estimated the
emissions reductions for the remaining five rules that could be made
more stringent to match the most stringent of the other district rules'
limits.\59\ Among the five source categories for which the District has
no current rules, the District identified four categories for which
other districts have adopted rules that could be adopted for Ventura
County.\60\
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\59\ The five District rules include Rule 74.2 (``Architectural
Coatings''), Rule 74.19.1 (``Screen Printing Operations''), Rule
74.21 (``Semiconductor Manufacturing''); Rule 74.22 (``Natural Gas-
Fired, Central Fan-Type Furnaces''), and Rule 74.34
(``NOX Reductions from Miscellaneous Sources'').
\60\ The four source categories include composting and organic
material conversion operations, vacuum truck operations, emissions
of oxides of nitrogen from commercial food ovens, and food products
manufacturing and processing operations.
---------------------------------------------------------------------------
The District estimated the potential emissions reduction associated
with revisions to the five existing District rules and adoption of the
four new rules to be approximately 0.5 tpd of VOC and 0.01 tpd of
NOX. Based on the District's threshold of 2 tpd of
NOX as the minimum reduction necessary to advance attainment
by one year, the District concluded that its current set of VOC and
NOX rules represent all RACM within regulatory jurisdiction,
and that no further RACM are necessary to meet the RACM requirement for
the 2008 ozone NAAQS. We note that the new stationary source control
measures in the 2016 Ventura County AQMP include revisions to two
existing District rules, Rule 74.2 (``Architectural Coatings'') and
Rule 74.22 (``Natural Gas-Fired, Central Fan-Type Furnaces''), and
adoption of one new rule, proposed new Rule 74.32 (``Compostable
Material Handing and Conversion Operations''), that are part of the
RACM analysis. However, the purpose of these stationary source control
measures in the 2016 Ventura County AQMP was not to meet the RACM
requirement but to provide emissions reductions for the 2015 ozone
NAAQS and to fulfill State air quality requirements.
b. Local Jurisdiction's RACM Analysis and Transportation Control
Measures
Transportation Control Measures (TCMs) are projects that reduce air
pollutants from transportation sources by reducing vehicle use, traffic
congestion, or vehicle miles traveled. Appendix B (``Ventura County
Transportation Control Measure Commitments'') of the 2016 Ventura
County AQMP lists the current TCMs identified by SCAG and the District
as committed TCMs. ``Committed'' TCMs are subject to the timely
implementation requirement in CAA section 176(c)(2)(B). For the 2016
Ventura County AQMP, the District and VCTC worked together to determine
whether additional TCMs are necessary to meet the RACM requirement. The
TCM RACM component of the 2016 Ventura County AQMP is found on page 55
of the AQMP and in Appendix F (``Ventura County Transportation Control
Measures Reasonably Available Control Measure Assessment'').
First, the District prepared a list of candidate RACM using the
CAA's list of TCMs in section 108(f)(1)(A) by reviewing the TCMs in the
2008 Ventura County AQMP, and other air district and planning agency
plans, such as the 2012 South Coast AQMP, 2007 San Joaquin Valley Ozone
Plan, 2013 Sacramento Regional 8-Hour Ozone Attainment and Reasonable
Further Progress Plan, and the 2004/2007 Metropolitan Washington
Council of Governments SIP. Second, the District, along with staff of
the VCTC, sorted the candidate TCMs based on their feasibility or
infeasibility for implementation in Ventura County.\61\ Table F-1 of
Appendix F of the 2016 Ventura County AQMP summarizes the results of
the sorting process. Justification is provided in Table F-1 for those
candidate TCMs deemed by the District and VCTC to be infeasible. All
candidate TCMs are organized in Table F-1 according to the sixteen
categories specified in section 108(f)(1)(A) of the CAA.
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\61\ See 2016 Ventura County AQMP, Appendix F, page F-1.
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The District found that the majority of TCMs that were deemed to be
feasible in Ventura County were already being implemented, or had been
implemented in the county, and that implementing all additional
feasible TCMs in the county would not advance attainment by a year.
Based on its comprehensive review of TCM projects in other
nonattainment areas or otherwise identified, the District determined
that the TCMs being implemented in Ventura County are inclusive of all
RACM.\62\
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\62\ See 2016 Ventura County AQMP, Appendix F, page F-3.
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c. CARB's RACM Analysis
Source categories for which CARB has primary jurisdiction for
reducing emissions in California include most new and existing on- and
off-road engines and vehicles, motor vehicle fuels, and consumer
products. CARB's RACM assessment is contained in the 2016 Ventura
County AQMP, Appendix G (``Ventura County Mobile Source Reasonably
Available Control Measures Assessment''). In the 2016 Ventura County
AQMP, CARB has also provided a general description of CARB's key mobile
source regulations and programs and a comprehensive table listing on-
and off-road mobile source regulatory actions taken by CARB from 1985
through 2016.\63\ The RACM assessment contains CARB's evaluation of
mobile source and other statewide control measures that reduce
emissions of NOX and VOC in Ventura County.
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\63\ See 2016 Ventura County AQMP, Appendix C (``Key ARB Mobile
Source Regulations and Programs'') and Appendix D (``Air Resources
Board Control Measures, 1985-2016'').
---------------------------------------------------------------------------
Given the need for substantial emissions reductions from mobile and
area sources to meet the NAAQS in California nonattainment areas, CARB
established stringent control measures for on-road and off-road mobile
sources and the fuels that power them. California has unique authority
under CAA section 209 (subject to a waiver by the EPA) to adopt and
implement new
[[Page 70118]]
emission standards for many categories of on-road vehicles and engines,
and new and in-use off-road vehicles and engines.
CARB's mobile source program extends beyond regulations that are
subject to the waiver or authorization process set forth in CAA section
209, to include standards and other requirements to control emissions
from in-use heavy-duty trucks and buses, gasoline and diesel fuel
specifications, and many other types of mobile sources. Generally,
these regulations have been submitted and approved as revisions to the
California SIP.\64\
---------------------------------------------------------------------------
\64\ See, e.g., the EPA's approval of standards and other
requirements to control emissions from in-use heavy-duty diesel-
powered trucks, at 77 FR 20308 (April 4, 2012), revisions to the
California on-road reformulated gasoline and diesel fuel regulations
at 75 FR 26653 (May 12, 2010), and revisions to the California motor
vehicle inspection and maintenance program at 75 FR 38023 (July 1,
2010).
---------------------------------------------------------------------------
In the RACM assessment, CARB concludes that there are no additional
RACM that would advance attainment of the 2008 ozone NAAQS in Ventura
County. As a result, CARB concludes that California's mobile source
programs fully meet the RACM requirement.\65\
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\65\ See 2016 Ventura County AQMP, Appendix G, page G-5.
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3. The EPA's Review of the State's Submission
As described above, the District already implements many rules to
reduce VOC and NOX emissions from stationary sources in
Ventura County. For the 2016 Ventura County AQMP, the District
evaluated a range of potentially available control measures. We find
that the process followed by the District in the 2016 Ventura County
AQMP to identify additional RACM is generally consistent with the EPA's
recommendations in the General Preamble, the District's evaluation of
potential measures is appropriate, and the District has provided
reasoned justifications for rejection of measures deemed not reasonably
available.
With respect to mobile sources, CARB's current program addresses
the full range of mobile sources in Ventura County through regulatory
programs for both new and in-use vehicles. With respect to TCMs, we
find that the District's and VCTC's process for identifying additional
TCM RACM and the District's conclusion that the TCMs being implemented
in Ventura County (i.e., the TCMs listed in Table B-1 in Appendix B of
the 2016 Ventura County AQMP) are inclusive of all TCM RACM to be
reasonably justified and supported.
Based on our review of these RACM analyses, the District's and
CARB's adopted rules, and SCAG's committed TCMs, we propose to find
that there are, at this time, no additional RACM that would advance
attainment of the 2008 ozone NAAQS in Ventura County.\66\ For the
foregoing reasons, we propose to find that the 2016 Ventura County AQMP
provides for the implementation of all RACM as required by CAA section
172(c)(1) and 40 CFR 51.1112(c).
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\66\ We find that the District's identification of a 2-tpd
threshold for the minimum reduction necessary to advance attainment
of the 2008 ozone NAAQS in Ventura County by one year to be
reasonable. The nonattainment area relies on both VOC and
NOX controls, and the potential emissions reductions of
NOX and VOC (considered together) from potential RACM
(stationary source, TCM, and mobile) would not achieve the necessary
emissions reductions to advance attainment by one year, and
therefore, such additional measures are not required to meet the
RACM requirement.
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D. Attainment Demonstration
1. Statutory and Regulatory Requirements
An attainment demonstration consists of the following: (1)
Technical analyses, such as base year and future year modeling, to
locate and identify sources of emissions that are contributing to
violations of the ozone NAAQS within the nonattainment area (i.e.,
analyses related to the emissions inventory for the nonattainment area
and the emissions reductions necessary to attain the standard); (2) a
list of adopted measures (including RACT controls) with schedules for
implementation and other means and techniques necessary and appropriate
for demonstrating RFP and attainment as expeditiously as practicable
but no later than the outside attainment date for the area's
classification; (3) a RACM analysis; and (4) contingency measures
required under sections 172(c)(9) and 182(c)(9) of the CAA that can be
implemented without further action by the state or the EPA to cover
emissions shortfalls in RFP plans and failures to attain.\67\ This
subsection of today's proposed rule addresses the first two components
of the attainment demonstration--the technical analyses and a list of
adopted measures. Section III.C, Reasonably Available Control Measures
Demonstration, of this document addresses the RACM component, and
section III.F, Contingency Measures, addresses the contingency measures
component of the attainment demonstration in the 2016 Ventura County
AQMP.
---------------------------------------------------------------------------
\67\ 78 FR 34178, at 34184 (June 6, 2013) (proposed rule for
implementing the 2008 ozone NAAQS).
---------------------------------------------------------------------------
With respect to the technical analyses, section 182(c)(2)(A) of the
CAA requires that a plan for an ozone nonattainment area classified
Serious or above include a ``demonstration that the plan . . . will
provide for attainment of the ozone [NAAQS] by the applicable
attainment date. This attainment demonstration must be based on
photochemical grid modeling or any other analytical method determined .
. . to be at least as effective.'' The attainment demonstration
predicts future ambient concentrations for comparison to the NAAQS,
making use of available information on measured concentrations,
meteorology, and current and projected emissions inventories of ozone
precursors, including the effect of control measures in the plan.
Areas classified Serious for the 2008 ozone NAAQS must demonstrate
attainment as expeditiously as practicable, but no later than 9 years
after the effective date of designation to nonattainment. Ventura
County was designated nonattainment effective July 20, 2012, and the
area must demonstrate attainment of the 2008 ozone NAAQS by July 20,
2021.\68\ An attainment demonstration must show attainment of the
standards for a full calendar year before the attainment date, so in
practice, Serious nonattainment areas must demonstrate attainment in
2020.
---------------------------------------------------------------------------
\68\ 80 FR 12264, at 12268 (March 6, 2015).
---------------------------------------------------------------------------
The EPA's recommended procedures for modeling ozone as part of an
attainment demonstration are contained in ``Modeling Guidance for
Demonstrating Attainment of Air Quality Goals for Ozone,
PM2.5, and Regional Haze'' (``Modeling Guidance'').\69\ The
Modeling Guidance includes recommendations for a modeling protocol,
model input preparation, model performance evaluation, use of model
output for the numerical NAAQS attainment test, and modeling
documentation. Air quality modeling is performed using meteorology and
emissions from a base year, and the predicted concentrations from this
base case modeling are compared to air quality monitoring data from
that year to evaluate model performance.
---------------------------------------------------------------------------
\69\ Modeling Guidance, December 2014 Draft, EPA OAQPS;
available at https://www.epa.gov/scram/state-implementation-plan-sip-attainment-demonstration-guidance. The 2014 modeling guidance
updates, but is largely consistent with, the earlier ``Guidance on
the Use of Models and Other Analyses for Demonstrating Attainment of
Air Quality Goals for the 8-Hour Ozone and PM2.5 NAAQS
and Regional Haze,'' EPA-454/B-07-002, April 2007. Additional EPA
modeling guidance can be found in 40 CFR 51 Appendix W, ``Guideline
on Air Quality Models,'' 82 FR 5182 (January 17, 2017); available at
https://www.epa.gov/scram/clean-air-act-permit-modeling-guidance.
---------------------------------------------------------------------------
Once the model performance is determined to be acceptable, future
year
[[Page 70119]]
emissions are simulated with the model. The relative (or percent)
change in modeled concentration due to future emissions reductions
provides a Relative Response Factor (RRF). Each monitoring site's RRF
is applied to its monitored base year design value to provide the
future design value for comparison to the NAAQS. The Modeling Guidance
also recommends supplemental air quality analyses, which may be used as
part of a Weight of Evidence (WOE) analysis. A WOE analysis
corroborates the attainment demonstration by considering evidence other
than the main air quality modeling attainment test, such as trends and
additional monitoring and modeling analyses.
The Modeling Guidance does not require a particular year to be used
as the base year for 2008 ozone NAAQS plans.\70\ The Modeling Guidance
states that the most recent year of the National Emissions Inventory
may be appropriate for use as the base year for modeling, but that
other years may be more appropriate when considering meteorology,
transport patterns, exceptional events, or other factors that may vary
from year to year.\71\ Therefore, the base year used for the attainment
demonstration need not be the same year used to meet the requirements
for RFP.
---------------------------------------------------------------------------
\70\ Modeling Guidance at section 2.7.1.
\71\ Ibid.
---------------------------------------------------------------------------
With respect to the list of adopted measures, CAA section 172(c)(6)
requires that nonattainment area plans include enforceable emissions
limitations, and such other control measures, means or techniques
(including economic incentives such as fees, marketable permits, and
auctions of emission rights), as well as schedules and timetables for
compliance, as may be necessary or appropriate to provide for timely
attainment of the NAAQS.\72\ Under the 2008 Ozone SRR, all control
measures needed for attainment must be implemented no later than the
beginning of the attainment year ozone season.\73\ The attainment year
ozone season is defined as the ozone season immediately preceding a
nonattainment area's maximum attainment date.\74\
---------------------------------------------------------------------------
\72\ See also CAA section 110(a)(2)(A).
\73\ 40 CFR 51.1108(d).
\74\ 40 CFR 51.1100(h).
---------------------------------------------------------------------------
2. Summary of the State's Submission
a. Photochemical Modeling
The 2016 Ventura County AQMP includes photochemical modeling for
the 2008 ozone NAAQS. The South Coast Air Quality Management District
(SCAQMD) performed the air quality modeling for the 2016 Ventura County
AQMP. The modeling relies on a 2012 base year and demonstrates
attainment of the 2008 ozone NAAQS by the applicable Serious area
attainment year (i.e. 2020).
The modeling and modeled attainment demonstration are described in
Chapter 5 (``Attainment Demonstration'') of the 2016 Ventura County
AQMP and in four appendices. Appendix H (``Protocol for Photochemical
Modeling of Ozone in Ventura County'') of the 2016 Ventura County AQMP
is the modeling protocol and contains all the elements recommended in
the Modeling Guidance. Those include: Selection of model, time period
to model, modeling domain, and model boundary conditions and
initialization procedures; a discussion of emissions inventory
development and other model input preparation procedures; model
performance evaluation procedures; selection of days; and other details
for calculating RRFs. Appendix H of the 2016 Ventura County AQMP also
provides the coordinates of the modeling domain and thoroughly
describes the development of the modeling emissions inventory,
including its chemical speciation, its spatial and temporal allocation,
its temperature dependence, and quality assurance procedures.
The modeling analysis used version 5.0.2 of the Community
Multiscale Air Quality (CMAQ) photochemical model, developed by the
EPA. To prepare meteorological input for CMAQ, the Weather and Research
Forecasting model version 3.6 (WRF) from the National Center for
Atmospheric Research was used. CMAQ and WRF are both recognized in the
Modeling Guidance as technically sound, state-of-the-art models. The
areal extent and the horizontal and vertical resolution used in these
models were adequate for modeling ozone in the southern California
domain, including Ventura.
The performance of the WRF meteorological model was assessed
through a series of simulations, and the SCAQMD concluded that the
daily WRF simulation for 2012 provided representative meteorological
fields that well characterized the observed conditions. The SCAQMD's
conclusions were supported by hourly time series graphs of wind speed,
direction, and temperature.\75\
---------------------------------------------------------------------------
\75\ SCAQMD, 2016 South Coast AQMP (March 2017), Appendix V
(``Modeling and Attainment Demonstration''), Chapter 3
(``Meteorological Modeling and Sensitivity Analyses''), Attachment 1
(``WRF Model Performance Time Series'').
---------------------------------------------------------------------------
Ozone model performance statistics are described in the 2016
Ventura County AQMP Appendix I (``Ventura County Community Multiscale
Air Quality Model Performance Analysis''), which include tables of
statistics recommended in the Modeling Guidance for 8-hour daily
maximum ozone for Ventura County. Hourly time series are presented, as
well as density scatter plots and plots of bias against concentration.
Note that only relative changes are used from the modeling, therefore
the overprediction or underprediction of absolute ozone concentrations
does not mean that future concentrations will be overestimated or
underestimated.
After model performance for the 2012 base case was accepted, the
model was applied to develop RRFs for the attainment demonstration.
This entailed running the model with the same meteorological inputs as
before, but with adjusted emissions inventories to reflect the expected
changes between 2012 and the 2020 attainment year. The base year or
``reference year'' modeling inventory was the same as the inventory for
the modeling base case. The 2020 inventory projects the base year into
the future by including the effect of economic growth and emissions
control measures. The set of 153 days from May 1 through September 30,
2012, was simulated and analyzed to determine daily 8-hour average
maximum ozone concentrations for the 2020 emissions inventory. To
develop the RRFs for the 2008 ozone NAAQS, only the top 10 days were
used.
The Modeling Guidance addresses attainment demonstrations with
ozone NAAQS based on 8-hour averages. For the 2008 ozone NAAQS, the
2016 Ventura County AQMP carried out the attainment test procedure
consistent with the Modeling Guidance. The RRFs were calculated as the
ratio of future to base year concentrations. The resulting RRFs were
then applied to 2012 weighted base year design values \76\ for each
monitor to arrive at a 2020 future year design value.\77\ The highest
2020 ozone design value is 0.072 ppm at the Simi Valley site; this
value demonstrates attainment of the
[[Page 70120]]
corresponding 2008 ozone NAAQS of 0.075 ppm.
---------------------------------------------------------------------------
\76\ The Modeling Guidance recommends that RRFs be applied to
the average of three three-year design values centered on the base
year, in this case the design values for 2010-2012, 2011-2013, and
2012-2014. This amounts to a 5-year weighted average of individual
year 4th-high concentrations, centered on the base year of 2012, and
so is referred to as a weighted design value.
\77\ 2016 Ventura County AQMP, Appendix I, Table I-2 (``Base
Year and Future Year Ozone Design Values'').
---------------------------------------------------------------------------
The 2016 Ventura County AQMP modeling also includes a WOE
demonstration in Appendix K (Ventura County Weight of Evidence
Assessment) prepared by CARB. To complement regional photochemical
modeling analyses included in the 2016 Ventura County AQMP, the WOE
demonstration includes detailed analyses of ambient ozone data, county
level precursor emissions trends, population exposure trends, and a
discussion of conditions that contribute to exceedances of the 0.075
ppm 2008 ozone NAAQS. Further, the rate of progress toward air quality
goals was evaluated by considering trends in ozone design values,
precursor emissions reductions, and the relationship between ozone air
quality and past emissions reductions.\78\
---------------------------------------------------------------------------
\78\ 2016 Ventura County AQMP, Appendix K, page K-2.
---------------------------------------------------------------------------
Finally, the 2016 Ventura County AQMP includes an unmonitored area
analysis for the 2008 ozone NAAQS to assess the attainment status of
locations other than monitoring sites.\79\ The Modeling Guidance
describes a ``gradient adjusted spatial fields'' procedure along with
the EPA software (i.e., Modeled Attainment Test Software) used to carry
it out.\80\ The unmonitored area analysis in the 2016 Ventura County
AQMP shows concentrations below the 2008 ozone NAAQS for all
locations.\81\
---------------------------------------------------------------------------
\79\ 2016 Ventura County AQMP, Appendix J (``Ventura County
Unmonitored Area Analysis''), prepared by the SCAQMD.
\80\ Modeling Guidance, section 4.7.
\81\ 2016 Ventura County AQMP, Appendix J, Figure J-3 (``2020
Predicted 8-hr Ozone Design Values'').
---------------------------------------------------------------------------
b. Control Strategy for Attainment
The control strategy for attainment of the 2008 ozone NAAQS in the
2016 Ventura County AQMP relies on emissions reductions from baseline
(i.e., already-adopted) measures. The baseline control measures include
the District's stationary source rules, including those specifically
included in the emissions inventories prepared for the 2016 Ventura
County AQMP,\82\ and CARB's mobile source and consumer product rules
adopted through 2016 as listed in Appendix D of the 2016 Ventura County
AQMP.
---------------------------------------------------------------------------
\82\ See 2016 Ventura County AQMP, Appendix A, Table A-5
(``District Rules Included in the SIP Inventory'').
---------------------------------------------------------------------------
c. Attainment Demonstration
Table 2 below summarizes the attainment demonstration for the 2008
ozone NAAQS by listing the base year (2012) emissions level, the
modeled attainment emissions level, and the reductions that the
District and CARB estimate to achieve through baseline control measures
taking into account growth and the District's ERC balance. As shown in
Table 2, baseline measures are expected to reduce base year (2012)
emissions of NOX by 21 percent and VOC emissions by 11
percent by the 2020 attainment year, notwithstanding growth and the ERC
balance, and to attain the 2008 ozone NAAQS in Ventura County by that
year.
Table 2--Summary of Ventura County 2008 Ozone NAAQS Attainment
Demonstration
[Summer planning inventory, tpd]
------------------------------------------------------------------------
NOX VOC
------------------------------------------------------------------------
A 2012 Base Year Emissions Level \a\.. 40.55 37.76.
B--2020 Modeled Attainment Emissions 32.06 33.50.
Level \a\.
C Total Reductions Needed from 2012 8.49 4.26.
Base Year Levels to Demonstrate
Attainment (A-B).
D Reductions from Baseline (i.e., 8.49 4.26.
adopted) Measures, net of growth and
ERC balance.
E 2020 Emissions with Reductions from 32.06 33.50.
Baseline Control Strategy (compare to
Row B).
Attainment demonstrated?.......... Yes Yes.
------------------------------------------------------------------------
Notes and sources:
\a\ 2016 Ventura County AQMP, Appendix A, tables A-6 and A-7. Includes
emissions out to 100 nautical miles from the coast. Year 2020 Modeled
Attainment Emissions Level includes ERC balance.
3. The EPA's Review of the State's Submission
a. Photochemical Modeling
To approve a SIP's attainment demonstration, the EPA must make
several findings. First, we must find that the demonstration's
technical bases, including the emissions inventories and air quality
modeling, are adequate. As discussed above in section III.A of this
document, we are proposing to approve the base year emissions inventory
and to find that the future year emissions projections in the 2016
Ventura County AQMP reflect appropriate calculation methods and that
the latest planning assumptions are properly supported by SIP-approved
stationary and mobile source measures. These are the same inventories
used for the attainment demonstration, and thus, we find that the
emissions portion of the attainment demonstration is adequate.
With respect to the photochemical modeling in the 2016 Ventura
County AQMP, based on our review of the 2016 Ventura County AQMP, the
EPA finds that the modeling is adequate for purposes of supporting the
attainment demonstration. First, we note the extensive discussion of
modeling procedures, tests, and performance analyses called for in the
Modeling Protocol (i.e., Appendix H) and the good model performance.
Second, we find the WRF meteorological model results and performance
statistics, including hourly time series graphs of wind speed,
direction, and temperature for the southern California modeling domain,
to be satisfactory and consistent with our Modeling Guidance.\83\
---------------------------------------------------------------------------
\83\ Modeling Guidance, 30.
---------------------------------------------------------------------------
The model performance statistics for ozone are described in the
2016 Ventura County AQMP, Appendix I. The analysis evaluated how well
the photochemical model for the 2016 Ventura County AQMP was able to
predict 8-hour ozone concentrations at each monitoring site in the
county compared to observed 8-hour ozone concentrations at those same
monitoring sites and is based on the statistical evaluation recommended
in the Modeling Guidance. The base year average regional model
performance was evaluated for May through September 2012 for days when
maximum 8-hour ozone levels were at least 60 ppb.\84\ Ozone
measurements from air quality monitors in Thousand Oaks, Piru, Ojai,
Simi Valley, and El Rio were compiled for the analysis. To develop the
RRFs for the 2008 ozone
[[Page 70121]]
NAAQS, only the top 10 days were used. This is consistent with EPA
guidance, which recommends the use of only the top 10 days in the RRF
calculation because the modeling capability to predict high
concentrations is more important than the prediction of low
concentrations.\85\
---------------------------------------------------------------------------
\84\ Only stations with more than 74.5% (the EPA's data
completeness requirement) of the hourly measurements during each
month of the ozone season were included in the analysis.
\85\ Modeling Guidance, 101.
---------------------------------------------------------------------------
The 2016 Ventura County AQMP's unmonitored area analysis showed
concentrations below the 2008 ozone NAAQS for all locations. This
analysis adds assurance to the attainment demonstration that all
locations in Ventura County will attain the 2008 ozone NAAQS by the
2020 attainment year. In addition, the WOE analyses presented in the
2016 Ventura County AQMP provide additional information with respect to
the sensitivity to emission changes and improve the understanding of
the model performance. We are proposing to find the air quality
modeling in the 2016 Ventura County AQMP adequate to support the
attainment demonstration for the 2008 ozone NAAQS in Ventura County,
based on reasonable meteorological and ozone modeling performance, and
further supported by the unmonitored area and WOE analyses.
b. Control Strategy for Attainment
Second, we must find that the emissions reductions that are relied
on for attainment are creditable and are sufficient to provide for
attainment. As shown in Table 2 above, the 2016 Ventura County AQMP
relies on baseline measures to achieve all the emissions reductions
needed to attain the 2008 ozone NAAQS by 2020. The baseline measures
are approved into the SIP and, as such, are fully creditable.
c. Attainment Demonstration
Based on our proposed determinations that the photochemical
modeling and control strategy are acceptable, we propose to approve the
attainment demonstration for the 2008 ozone NAAQS in the 2016 Ventura
County AQMP as meeting the requirements of CAA section 182(c)(2)(A) and
40 CFR 51.1108.
E. Rate of Progress Plan and Reasonable Further Progress Demonstration
1. Statutory and Regulatory Requirements
Requirements for RFP for ozone nonattainment areas are specified in
CAA sections 172(c)(2), 182(b)(1), and 182(c)(2)(B). Under CAA section
171(1), RFP is defined as meaning such annual incremental reductions in
emissions of the relevant air pollutant as are required under CAA part
D (``Plan Requirements for Nonattainment Areas'') or may reasonably be
required by the EPA for the purpose of ensuring attainment of the
applicable NAAQS by the applicable date. CAA section 172(c)(2)
generally requires that a nonattainment plan include provisions for
RFP. CAA section 182(b)(1) specifically requires that ozone
nonattainment areas that are classified as Moderate or above
demonstrate a 15 percent reduction in VOC between the years of 1990 and
1996. The EPA has typically referred to section 182(b)(1) as the rate
of progress (ROP) requirement. For ozone nonattainment areas classified
as Serious or higher, section 182(c)(2)(B) requires reductions averaged
over each consecutive 3-year period, beginning 6 years after the
baseline year until the attainment date, of at least 3 percent of
baseline emissions per year. The provisions in CAA section
182(c)(2)(B)(ii) allow an amount less than 3 percent of such baseline
emissions each year if the state demonstrates to the EPA that the plan
includes all measures that can feasibly be implemented in the area in
light of technological achievability.
In the 2008 Ozone SRR, the EPA provides that areas classified
Moderate or higher for the 2008 ozone NAAQS will have met the ROP
requirements of CAA section 182(b)(1) if the area has a fully approved
15 percent ROP plan for the 1-hour or 1997 ozone NAAQS, provided that
the boundaries of the ozone nonattainment areas are the same.\86\ For
such areas, the EPA interprets the RFP requirements of CAA section
172(c)(2) to require areas classified as Moderate to provide a 15
percent emission reduction of ozone precursors within 6 years of the
baseline year. Areas classified as Serious or higher must meet the RFP
requirements of CAA section 182(c)(2)(B) by providing an 18 percent
reduction of ozone precursors in the first 6-year period, and an
average ozone precursor emission reduction of 3 percent per year for
all remaining 3-year periods thereafter.\87\ To meet CAA sections
172(c)(2) and 182(c)(2)(B) RFP requirements, the state may substitute
NOX emissions reductions for VOC reductions.\88\
---------------------------------------------------------------------------
\86\ 70 FR 12264, at 12271 (March 6, 2015).
\87\ Id.
\88\ 40 CFR 51.1110(a)(2)(i)(C) and 40 CFR 51.1110(a)(2)(ii)(B);
and 70 FR 12264, at 12271 (March 6, 2015).
---------------------------------------------------------------------------
Except as specifically provided in CAA section 182(b)(1)(C),
emissions reductions from all SIP-approved, federally promulgated, or
otherwise SIP-creditable measures that occur after the baseline year
are creditable for purposes of demonstrating that the RFP targets are
met. Because the EPA has determined that the passage of time has caused
the effect of certain exclusions to be de minimis, the RFP
demonstration is no longer required to calculate and specifically
exclude reductions from measures related to motor vehicle exhaust or
evaporative emissions promulgated by January 1, 1990; regulations
concerning Reid vapor pressure promulgated by November 15, 1990;
measures to correct previous RACT requirements; and, measures required
to correct previous inspection and maintenance (I/M) programs.\89\
---------------------------------------------------------------------------
\89\ 40 CFR 51.1110(a)(7).
---------------------------------------------------------------------------
The 2008 Ozone SRR requires the RFP baseline year to be the most
recent calendar year for which a complete triennial inventory was
required to be submitted to the EPA. For the purposes of developing RFP
demonstrations for the 2008 ozone NAAQS, the applicable triennial
inventory year is 2011. As discussed previously, the 2008 Ozone SRR
provided states with the opportunity to use an alternative baseline
year for RFP,\90\ but that provision of the 2008 Ozone SRR was vacated
by the D.C. Circuit in the South Coast II decision.
---------------------------------------------------------------------------
\90\ 40 CFR 51.1110(b).
---------------------------------------------------------------------------
2. Summary of the State's Submission
The 2016 Ventura County AQMP addresses both the ROP (VOC only)
demonstration requirement and the RFP demonstration requirement. With
respect to the former, the District cites the EPA's 1997 approval of
the ROP demonstration for the 1-hour ozone NAAQS for Ventura County and
concludes that, based on the 1997 approval, the ROP requirement has
been met for Ventura County for the 2008 ozone NAAQS.\91\
---------------------------------------------------------------------------
\91\ See 2016 Ventura County AQMP, 89, and 62 FR 1150 (January
8, 1997).
---------------------------------------------------------------------------
With respect to the RFP demonstration requirement, the 2016 Ventura
County AQMP includes an RFP demonstration derived from a 2012 RFP
baseline year.\92\ In response to the South Coast II decision, CARB
developed the 2018 SIP Update, which includes a section that replaces
the RFP portion of the 2016 Ventura County AQMP and includes emissions
estimates for the RFP baseline year, subsequent milestone years, and
the attainment year, and an updated RFP demonstration based on
[[Page 70122]]
the 2011 RFP baseline year.\93\ To develop the 2011 RFP baseline
inventory, CARB relied on actual emissions reported from industrial
point sources for year 2011. For emissions from smaller stationary
sources and area sources, CARB backcast emissions from 2012 to 2011
using the same growth and control factors as were used for the 2016
Ventura County AQMP. To develop the emissions inventories for the 2017
RFP milestone year and 2020 RFP milestone/attainment year, CARB also
relied upon the same growth and control factors as the 2016 Ventura
County AQMP.
---------------------------------------------------------------------------
\92\ See 2016 Ventura County AQMP, chapter 6 (``Reasonable
Further Progress'').
\93\ 2018 SIP Update, RFP demonstration, chapter III (``SIP
Elements for Ventura County''), section III-B (``Reasonable Further
Progress'').
---------------------------------------------------------------------------
Documentation for the Ventura County RFP baseline and milestone
emissions inventories is found in the 2018 SIP Update on pages 15-18
and Appendix A on pages A-7 through A-10. For both sets of baseline
emissions inventories (those in the 2016 Ventura County AQMP and those
in the 2018 SIP Update), emissions estimates reflect District rules
adopted through July 2015 and CARB rules adopted through November 2015.
Unlike the emissions inventories for the attainment demonstration in
the 2016 Ventura County AQMP, the RFP baseline and milestone emissions
inventories only include emissions within the Ventura County ozone
nonattainment area and do not include marine emissions (e.g., emissions
from ocean-going vessels) beyond three nautical miles from the
coastline. In contrast, the attainment demonstration inventories
include emissions from marine vessels out to 100 nautical miles from
the coastline.
Table 3 provides a summary of CARB's 2011 RFP baseline year, 2017
RFP milestone year, and 2020 RFP milestone/attainment year emissions
estimates in tpd for VOC and NOX.
Table 3--Ventura County 2011 Base Year, 2017 RFP Milestone Year and 2020 Attainment Year Emissions Inventories
[Summer planning inventory, tpd]
----------------------------------------------------------------------------------------------------------------
2011 2017 2020
Category -----------------------------------------------------------------
VOC NOX VOC NOX VOC NOX
----------------------------------------------------------------------------------------------------------------
Stationary.................................... 8.4 2.0 8.4 1.9 8.6 1.9
Area Sources.................................. 11.7 1.0 10.8 0.7 11.0 0.6
On-Road Mobile Sources........................ 9.2 13.9 5.4 8.0 4.2 6.0
Other (Off-Road) Mobile Sources............... 8.7 9.2 7.2 7.9 6.6 7.3
Total (not including ERC balance)............. 38.1 26.0 31.7 18.5 30.4 15.8
ERC Balance................................... ......... ......... ......... ......... 1.7 0.8
Total (including ERC balance)............. 38.1 26.0 31.7 18.5 32.1 16.6
----------------------------------------------------------------------------------------------------------------
Source: 2018 SIP Update, pp. 15-18 and Appendix A, pp. A-7--A-10. The sum of the emissions values may not equal
the total shown due to rounding of the numbers.
In August 2019, CARB provided a technical clarification of the RFP
demonstration in the 2018 SIP Update for Ventura County.\94\
Specifically, CARB revised the RFP demonstration in the 2018 SIP Update
to include the safety margin included in the 2020 motor vehicle
emissions budgets in the 2016 Ventura County AQMP. Table 4 presents the
updated RFP demonstration for Ventura County for the 2008 ozone NAAQS
as clarified by CARB in August 2019.
---------------------------------------------------------------------------
\94\ Letter dated August 29, 2019, from Dr. Michael T. Benjamin,
Chief, Air Quality Planning and Science Division, CARB, to Amy
Zimpfer, Assistant Director, Air Division, EPA Region IX.
Table 4--RFP Demonstration for Ventura County for the 2008 Ozone NAAQS
[Summer planning inventory, tpd or percent]
----------------------------------------------------------------------------------------------------------------
VOC
-----------------------------------------------------------------------------
2011 2017 2020
----------------------------------------------------------------------------------------------------------------
Baseline VOC \a\.................. 38.1.................... 31.7.................... 32.1
2020 Transportation Conformity ........................ ........................ 0.7
Rounding Margin \b\.
Baseline VOC + Rounding Margin.... ........................ 31.7.................... 32.8
Required change since 2011 (VOC or ........................ 18%..................... 27%
NOX), %.
Target VOC level.................. ........................ 31.2.................... 27.8
Apparent shortfall (-)/surplus (+) ........................ -0.5.................... -5.0
in VOC.
Apparent shortfall (-)/surplus (+) ........................ -1.4%................... -13.2%
in VOC, %.
VOC shortfall previously provided ........................ 0.0%.................... 1.4%
by NOX substitution, %.
Actual VOC shortfall (-)/surplus ........................ -1.4%................... -11.7%
(+), %.
----------------------------------------------------------------------------------------------------------------
NOX
-----------------------------------------------------------------------------
2011 2017 2020
----------------------------------------------------------------------------------------------------------------
Baseline NOX \a\.................. 26.0.................... 18.5.................... 16.6
2020 Transportation Conformity ........................ ........................ 0.9
Rounding Margin \b\.
Baseline NOX + Rounding Margin.... ........................ 18.5.................... 17.5
Change in NOX since 2011.......... ........................ 7.5..................... 8.5
Change in NOX since 2011, %....... ........................ 28.8%................... 32.8%
NOX reductions used for VOC ........................ 0%...................... 1.4%
substitution through last
milestone year, %.
NOX reductions since 2011 ........................ 28.8%................... 31.4%
available for VOC substitution in
this milestone year, %.
[[Page 70123]]
NOX reductions since 2011 used for ........................ 1.4%.................... 11.7%
VOC substitution in this
milestone year, %.
NOX reductions since 2011 surplus ........................ 27.4%................... 19.6%
after meeting VOC substitution
needs in this milestone year, %.
Total shortfall for RFP........... ........................ 0%...................... 0%
RFP met?.......................... ........................ Yes..................... Yes
----------------------------------------------------------------------------------------------------------------
Source: Letter dated August 29, 2019, from Dr. Michael T. Benjamin, Chief, Air Quality Planning and Science
Division, CARB, to Amy Zimpfer, Assistant Director, Air Division, EPA Region IX, Attachment A.
\a\ 2020 projections include addition of ERC balance as of January 1, 2012.
\b\ Transportation conformity rounding margin is referred to herein as a ``safety margin.''
The revised RFP demonstration calculates future year VOC targets
from the 2011 baseline, consistent with CAA 182(c)(2)(B)(i), which
requires reductions of ``at least 3 percent of baseline emissions each
year;'' and it substitutes NOX reductions for VOC reductions
beginning in milestone year 2017 to meet VOC emission targets.\95\ For
Ventura County, CARB concludes that the revised RFP demonstration meets
the applicable requirements for each milestone year as well as the
attainment year.
---------------------------------------------------------------------------
\95\ NOX substitution is permitted under EPA
regulations. See 40 CFR 51.1110(a)(2)(i)(C) and 40 CFR
51.1110(a)(2)(ii)(B); and 70 FR 12264, at 12271 (March 6, 2015).
---------------------------------------------------------------------------
3. The EPA's Review of the State's Submission
In 1997, the EPA approved a 15 percent ROP plan for the Ventura
County ozone nonattainment area for the 1-hour ozone NAAQS, and the
Ventura County nonattainment area for the 2008 ozone NAAQS is the same
as the Ventura County nonattainment area for the 1-hour ozone
NAAQS.\96\ As a result, we agree with the District that the District
and CARB have met the ROP requirements of CAA section 182(b)(1) for
Ventura County with respect to the 2008 ozone NAAQS.
---------------------------------------------------------------------------
\96\ 62 FR 1150, at 1183 (January 8, 1997).
---------------------------------------------------------------------------
With respect to the RFP demonstration requirement, based on our
review of the emissions inventory documentation in the 2016 Ventura
County Ozone SIP, we find that CARB and the District have used the most
recent planning and activity assumptions, emissions models, and
methodologies in developing the RFP baseline and milestone year
emissions inventories. We have also reviewed the calculations in Table
III-3 of the 2018 SIP Update, as clarified by CARB in August 2019, and
find that CARB has used an appropriate calculation method to
demonstrate RFP.\97\ For these reasons, we have determined that the
2016 Ventura County Ozone SIP, as clarified by CARB in August 2019,
demonstrates RFP in the 2017 milestone year and the 2020 milestone/
attainment year, consistent with applicable CAA requirements and EPA
guidance. Therefore, we propose to approve the RFP demonstration for
Ventura County for the 2008 ozone NAAQS under sections 172(c)(2) and
182(c)(2)(B) of the CAA and 40 CFR 51.1110(a)(2)(ii).
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\97\ We note a minor discrepancy between the safety margins
included in the revised RFP demonstration for the 2020 attainment
year and the safety margins included in the motor vehicle emissions
budgets for 2020 in the 2016 Ventura County AQMP. The safety margins
for the RFP demonstration, as shown in Table 4 of this document, are
0.7 tpd for VOC and 0.9 tpd for NOX. The safety margins
for the motor vehicle emissions budgets in the 2016 Ventura County
AQMP are 0.79 tpd for VOC (0.8 tpd, if rounded to one significant
figure) and 0.99 tpd (1.0 tpd, if rounded). Given the substantial
extent to which the 2016 Ventura County Ozone SIP provides emissions
reductions in excess of the RFP milestones, this minor discrepancy
does not change our proposed finding that the 2016 Ventura County
Ozone SIP meets the RFP demonstration requirement for the 2008 ozone
NAAQS.
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F. Contingency Measures
1. Statutory and Regulatory Requirements
Under the CAA, 8-hour ozone nonattainment areas classified under
subpart 2 as Moderate or above must include in their SIPs contingency
measures consistent with sections 172(c)(9) and 182(c)(9). Contingency
measures are additional controls or measures to be implemented in the
event the area fails to make reasonable further progress or to attain
the NAAQS by the attainment date. The SIP should contain trigger
mechanisms for the contingency measures, specify a schedule for
implementation, and indicate that the measure will be implemented
without significant further action by the state or the EPA.\98\
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\98\ 70 FR 71612 (November 29, 2005). See also 2008 Ozone SRR,
80 FR 12264, at 12285 (March 6, 2015).
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Neither the CAA nor the EPA's implementing regulations establish a
specific level of emissions reductions that implementation of
contingency measures must achieve, but the EPA's 2008 Ozone SRR
reiterates the EPA's policy that contingency measures should provide
for emissions reductions approximately equivalent to one year's worth
of progress, amounting to reductions of 3 percent of the RFP baseline
emissions inventory for the nonattainment area.\99\
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\99\ 80 FR 12264, at 12285 (March 6, 2015).
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It has been the EPA's longstanding interpretation of section
172(c)(9) that states may rely on federal measures (e.g., federal
mobile source measures based on the incremental turnover of the motor
vehicle fleet each year) and local measures already scheduled for
implementation that provide emissions reductions in excess of those
needed to provide for RFP or expeditious attainment. The key is that
the statute requires that contingency measures provide for additional
emissions reductions that are not relied on for RFP or attainment and
that are not included in the RFP or attainment demonstrations. The
purpose of contingency measures is to provide continued emissions
reductions while the plan is being revised to meet the missed milestone
or attainment date.
The EPA has approved numerous SIPs under this interpretation--i.e.,
SIPs that use as contingency measures one or more federal or local
measures that are in place and provide reductions that are in excess of
the reductions required by the attainment demonstration or RFP
plan,\100\ and there is case law supporting the EPA's interpretation in
this regard.\101\ However, in Bahr v. EPA, the Ninth Circuit rejected
the EPA's interpretation of CAA section 172(c)(9) as allowing for early
implementation of
[[Page 70124]]
contingency measures.\102\ The Ninth Circuit concluded that contingency
measures must take effect at the time the area fails to make RFP or
attain by the applicable attainment date, not before.\103\ Thus, within
the geographic jurisdiction of the Ninth Circuit, states cannot rely on
early-implemented measures to comply with the contingency measure
requirements under CAA section 172(c)(9) and 182(c)(9).\104\
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\100\ See, e.g., 62 FR 15844 (April 3, 1997) (direct final rule
approving an Indiana ozone SIP revision); 62 FR 66279 (December 18,
1997) (final rule approving an Illinois ozone SIP revision); 66 FR
30811 (June 8, 2001) (direct final rule approving a Rhode Island
ozone SIP revision); 66 FR 586 (January 3, 2001) (final rule
approving District of Columbia, Maryland, and Virginia ozone SIP
revisions); and 66 FR 634 (January 3, 2001) (final rule approving a
Connecticut ozone SIP revision).
\101\ See, e.g., LEAN v. EPA, 382 F.3d 575 (5th Cir. 2004)
(upholding contingency measures that were previously required and
implemented where they were in excess of the attainment
demonstration and RFP SIP).
\102\ Bahr v. EPA, 836 F.3d 1218, at 1235-1237 (9th Cir. 2016).
\103\ Id. at 1235-1237.
\104\ The Bahr v. EPA decision involved a challenge to an EPA
approval of contingency measures under the general nonattainment
area plan provisions for contingency measures in CAA section
172(c)(9), but, given the similarity between the statutory language
in section 172(c)(9) and the ozone-specific contingency measure
provision in section 182(c)(9), we find that the decision affects
how both sections of the Act must be interpreted.
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2. Summary of the State's Submission
The District and CARB had largely prepared the 2016 Ventura County
Ozone SIP prior to the Bahr v. EPA decision, and thus, consistent with
contingency measure elements of previous ozone plans, it relies solely
upon surplus emissions reductions from already-implemented control
measures to demonstrate compliance with the contingency measure
requirements of CAA sections 172(c)(9) and 182(c)(9).\105\
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\105\ 2016 Ventura County AQMP, chapter 7 (``Contingency
Measures''), 91 and 92.
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In the 2018 SIP Update, CARB revises the RFP demonstration for the
2008 ozone NAAQS for Ventura County and recalculates the extent of
surplus emission reductions (i.e., surplus to meeting the RFP milestone
requirement for a given milestone year) in the milestone years and
estimates the incremental emissions reductions in the year following
the attainment year. In light of the Bahr v. EPA decision, however, the
2018 SIP Update does not rely on the surplus or incremental emissions
reductions to comply with the contingency measures requirements of
sections 172(c)(9) and 182(c)(9) but, rather, to provide context in
which to evaluate the adequacy of Bahr-compliant (i.e., to take effect
if triggered) contingency measures for the 2008 ozone NAAQS.\106\
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\106\ 2018 SIP Update, chapter III (``SIP Elements for Ventura
County''), 18-20.
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To comply with CAA sections 172(c)(9) and 182(c)(9), as interpreted
in the Bahr v. EPA decision, the state must develop, adopt, and submit
a contingency measure to be triggered upon a failure to meet an RFP
milestone or attain the NAAQS by the applicable attainment date
regardless of the extent to which already-implemented measures would
achieve surplus or incremental emissions reductions beyond those
necessary for RFP or attainment of the NAAQS. Therefore, to fully
address the contingency measure requirement for the 2008 ozone NAAQS in
Ventura County, the District has committed to supplement the
contingency measure element of the 2016 Ventura County Ozone SIP by
developing, adopting and submitting a contingency measure to CARB in
sufficient time to allow CARB to submit the contingency measure as a
SIP revision to the EPA within 12 months of the EPA's conditional
approval of the contingency measure element of the 2016 Ventura County
Ozone SIP.\107\
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\107\ Letter dated August 16, 2019, from Michael Villegas, Air
Pollution Control Officer, VCAPCD, to Richard Corey, Executive
Officer, CARB.
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The District's specific commitment is to amend at least one of the
following existing VCAPCD rules, through the required public review and
subsequent VCAPCD board approval processes, to apply more stringent
requirements upon a determination that the Ventura County nonattainment
area failed to meet an RFP milestone or failed to attain the 2008 ozone
NAAQS by the applicable attainment date.
Amendments to Rule 74.26 (``Crude Oil Storage Tank
Degassing Operations'') to add, if triggered by an RFP milestone
failure or a failure to attain the 2008 ozone NAAQS, requirements for
reducing VOC emissions from certain operations not covered by the
existing rule, including cleaning, removing, repair and depressurizing
of pipelines;
Amendments to Rule 74.14 (``Polyester Resin Material
Operations'') to add a non-monomer content VOC limit of no more than 5
percent by weight, if triggered; or
Amendments to Rule 74.2 (``Architectural Coatings'') to
lower the VOC limit for coating categories; delete the Specialty
Primer, Sealer, and Undercoater categories and regulate them as just
primers, sealers and undercoaters; add the specialty coating categories
(Interior Stains, and Tile and Stone Sealers); and lower certain VOC
content limits for colorants, once again, if triggered.
CARB attached the District's commitment to revise a rule to include
contingency provisions to a letter committing CARB to adopt and submit
the revised VCAPCD rule or rules to the EPA within one year of the
effective date of the EPA's final conditional approval of the
contingency measure element of the 2016 Ventura County Ozone SIP.\108\
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\108\ Letter dated August 30, 2019, from Richard W. Corey,
Executive Officer, CARB, to Mike Stoker, Regional Administrator, EPA
Region IX.
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3. The EPA's Review of the State's Submission
Sections 172(c)(9) and 182(c)(9) require contingency measures to
address potential failure to achieve RFP milestones or failure to
attain the NAAQS by the applicable attainment date. For the purposes of
evaluating the contingency measure element of the 2016 Ventura County
Ozone SIP, we find it useful to distinguish between contingency
measures to address potential failure to achieve RFP milestones (``RFP
contingency measures'') and contingency measures to address potential
failure to attain the NAAQS (``attainment contingency measures'').
With respect to the RFP contingency measure requirement, we have
reviewed the surplus emissions estimates in each of the RFP milestone
years, as shown in the 2018 SIP Update (and clarified in August 2019),
and find that the calculations are correct. Therefore, we agree that
the 2016 Ventura County Ozone SIP provides surplus emissions reductions
well beyond those necessary to demonstrate RFP in the RFP milestone
years. While such surplus emissions reductions in the RFP milestone
years do not represent contingency measures themselves, we believe they
are relevant in evaluating the adequacy of RFP contingency measures
that are submitted (or will be submitted) to meet the requirements of
sections 172(c)(9) and 182(c)(9).
In this case, the District and CARB have committed to develop,
adopt, and submit a revised District rule or rules as a contingency
measure within one year of the effective date of our final conditional
approval action. The specific types of revisions the District has
committed to make, such as adding new limits or other requirements,
upon a failure to achieve a milestone or a failure to attain would
comply with the requirements in CAA sections 172(c)(9) and 182(c)(9)
because they would be undertaken if the area fails to attain and would
take effect without significant further action by the State or the EPA.
Next, we considered the adequacy of the RFP contingency measure
(once adopted and submitted) from the standpoint of the magnitude of
emissions reductions the measure would provide (if triggered). Neither
the CAA nor the EPA's implementing regulations for the ozone NAAQS
[[Page 70125]]
establish a specific amount of emissions reductions that implementation
of contingency measures must achieve, but we generally expect that
contingency measures should provide for emissions reductions
approximately equivalent to one year's worth of RFP, which, for ozone,
amounts to reductions of 3 percent of the RFP baseline year emissions
inventory for the nonattainment area. For the 2008 ozone NAAQS in
Ventura County, one year's worth of RFP is approximately 1.1 tpd of VOC
or 0.8 tpd of NOX reductions.\109\
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\109\ One year's worth of RFP for Ventura County corresponds to
3 percent of the RFP baseline year inventories for VOC (38.1 tpd)
and NOX (26.0 tpd).
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The District did not quantify the potential additional emission
reductions from its contingency measure commitment, but we believe that
it is unlikely that the attainment contingency measure, once adopted
and submitted, will achieve one year's worth of RFP (i.e., 1.1 tpd of
VOC or 0.8 tpd of NOX) given the types of rule revisions
under consideration and the magnitude of emissions reductions
constituting one year's worth of RFP. However, the 2018 SIP Update
provides the larger SIP planning context in which to judge the adequacy
of the to-be-submitted District contingency measure by calculating the
surplus emissions reductions estimated to be achieved in the RFP
milestone years and the year after the attainment year. More
specifically, the 2018 SIP Update, as clarified by CARB in August 2019,
identified surplus NOX reductions in the various RFP
milestone years. For Ventura County, the estimates of surplus
NOX reductions are 7.1 tpd in 2017 and 6.5 tpd in 2020 and
are 8 or 9 times greater than one year's worth of progress (0.8 tpd of
NOX).\110\
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\110\ For the 2017 and 2020 RFP milestone years, surplus
NOX reductions correspond to 27.4 percent and 24.9
percent, respectively, of the 26.0 tpd 2011 RFP milestone inventory.
See Table 4 in section III.E of this document.
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The surplus reflects already implemented regulations and is
primarily the result of vehicle turnover, which refers to the ongoing
replacement by individuals, companies, and government agencies of
older, more polluting vehicles and engines with newer vehicles and
engines. In light of the extent of surplus NOX emissions
reductions in the RFP milestone years, the emissions reductions from
the District contingency measure would be sufficient to meet the
contingency measure requirements of the CAA with respect to RFP
milestones, even though the measure would likely achieve emissions
reductions lower than the EPA normally recommends for reductions from
such a measure.
For attainment contingency measure purposes, we view the emissions
reductions from the contingency measure in the context of the expected
reduction in emissions within Ventura County in the year following the
attainment year relative to those occuring in the attainment year.
Based on the emission inventories in Appendix A to the 2018 SIP Update,
we note that overall county-wide emissions are expected to be
approximately 0.9 tpd of NOX lower in 2021 than in 2020.
Thus, baseline measures are expected to provide for continued progress
(i.e., incremental reduction in ozone precursors) greater than one
year's worth of progress (i.e., 0.8 tpd of NOX). In light of
these incremental year-over-year NOX emissions reductions,
we find that the emissions reductions from the District contingency
measure would also be sufficient to meet the attainment contingency
measure requirement of the CAA, even though the measure would likely
achieve emissions reductions lower than the EPA normally recommends for
reductions from such a measure.
For these reasons, we propose to approve conditionally the
contingency measure element of the 2016 Ventura County Ozone SIP, as
supplemented by commitments from the District and CARB to adopt and
submit an additional contingency measure, to meet the contingency
measure requirements of CAA sections 172(c)(9) and 182(c)(9). Our
proposed approval is conditional because it relies upon commitments to
adopt and submit a specific enforceable contingency measure (i.e., a
revised District rule or rules with contingent provisions). Conditional
approvals are authorized under CAA section 110(k)(4).
G. Motor Vehicle Emissions Budgets for Transportation Conformity
1. Statutory and Regulatory Requirements
Section 176(c) of the CAA requires federal actions in nonattainment
and maintenance areas to conform to the SIP's goals of eliminating or
reducing the severity and number of violations of the NAAQS and
achieving timely attainment of the standards. Conformity to the SIP's
goals means that such actions will not: (1) Cause or contribute to
violations of a NAAQS, (2) worsen the severity of an existing
violation, or (3) delay timely attainment of any NAAQS or any interim
milestone.
Actions involving Federal Highway Administration (FHWA) or Federal
Transit Administration (FTA) funding or approval are subject to the
EPA's transportation conformity rule, codified at 40 CFR part 93,
subpart A. Under this rule, MPOs in nonattainment and maintenance areas
coordinate with state and local air quality and transportation
agencies, the EPA, the FHWA, and the FTA to demonstrate that an area's
regional transportation plans and transportation improvement programs
conform to the applicable SIP. This demonstration is typically done by
showing that estimated emissions from existing and planned highway and
transit systems are less than or equal to the motor vehicle emissions
budgets (``budgets'') contained in all control strategy SIPs. Budgets
are generally established for specific years and specific pollutants or
precursors. Ozone plans should identify budgets for on-road emissions
of ozone precursors (NOX and VOC) in the area for each RFP
milestone year and, if the plan demonstrates attainment, the attainment
year.\111\
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\111\ 40 CFR 93.102(b)(2)(i).
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For budgets to be approvable, they must meet, at a minimum, the
EPA's adequacy criteria (40 CFR 93.118(e)(4)). To meet these
requirements, the budgets must be consistent with the attainment and
RFP requirements and reflect all of the motor vehicle control measures
contained in the attainment and RFP demonstrations.\112\
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\112\ 40 CFR 93.118(e)(4)(iii), (iv) and (v). For more
information on the transportation conformity requirements and
applicable policies on budgets, please visit our transportation
conformity website at: https://www.epa.gov/otaq/stateresources/transconf/index.htm.
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The EPA's process for determining adequacy of a budget consists of
three basic steps: (1) Providing public notification of a SIP
submission; (2) providing the public the opportunity to comment on the
budget during a public comment period; and, (3) making a finding of
adequacy or inadequacy.\113\
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\113\ 40 CFR 93.118(f)(2).
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2. Summary of the State's Submission
The 2016 Ventura County AQMP includes budgets for the 2018 RFP
milestone year and the 2020 attainment year.\114\ The budgets for 2018
were derived from the 2012 RFP baseline year and the associated 2018
RFP milestone year. As such, the budgets are affected by the South
Coast II decision vacating
[[Page 70126]]
the alternative baseline year provision, and therefore, the EPA has not
previously acted on the budgets. In the submittal letter for the 2016
Ventura County AQMP, CARB requested that the EPA limit the duration of
our approval of the budgets in the 2016 Ventura County AQMP to last
only until the effective date of future EPA adequacy findings for
replacement budgets.\115\ In August 2019, CARB provided further
explanation in connection with its request to limit the duration of the
approval of the budgets in the 2016 Ventura County AQMP.\116\
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\114\ When the 2016 Ventura County AQMP was developed, 2012 was
used as the RFP baseline year, and 2020 was not considered an RFP
milestone year because it was not one of the years that follow in
the three-year cycle after the initial six-year period after the RFP
baseline year. However, in the wake of the South Coast II decision,
2011 became the required RFP baseline year and year 2020 became an
RFP milestone year because it is three years after the initial six-
year period from the 2011 RFP baseline year. Thus, the 2020 budgets
from the 2016 Ventura County AQMP now serve as both the RFP
milestone and attainment budgets.
\115\ Letter dated April 11, 2017, from Richard Corey, Executive
Officer, CARB, to Alexis Strauss, Acting Regional Administrator, EPA
Region IX, transmitting the 2016 Ventura County AQMP.
\116\ Letter dated August 29, 2019, from Dr. Michael T.
Benjamin, Chief, Air Quality Planning and Science Division, CARB, to
Amy Zimpfer, Assistant Director, Air Division, EPA Region IX.
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On December 5, 2018, CARB submitted the 2018 SIP Update, which
revised the RFP demonstration consistent with the South Coast II
decision (i.e., by using a 2011 RFP baseline year). The 2018 SIP Update
does not identify new budgets for Ventura County for VOC and
NOX for the 2017 RFP milestone year because budgets for the
2017 milestone year would never be used for conformity determinations
given that milestone/attainment budgets for the immediate near-term
year of 2020 have also been submitted. Today, we are proposing action
only on the 2020 RFP milestone/attainment budgets from the 2016 Ventura
County AQMP.
The budgets in the 2016 Ventura County AQMP were derived from motor
vehicle emissions estimates prepared using EMFAC2014,\117\ and the
travel activity data provided by SCAG. The conformity budgets for
NOX and VOC in the 2016 Ventura County AQMP for Ventura
County in 2020 are provided in Table 5 below. To develop the budgets,
the District rounded up the motor vehicle emissions estimates for 2020
to the nearest ton. Thus, the motor vehicle emissions estimates for
Ventura County for VOC and NOX in 2020, i.e., 4.21 tpd and
6.01 tpd, respectively, were rounded up to become budgets for VOC and
NOX of 5 tpd and 7 tpd, respectively.
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\117\ As previously noted, EMFAC2014 is CARB's model for
estimating emissions from on-road vehicles operating in California.
See 80 FR 77337 (December 14, 2015). We have recently announced the
availability of an updated version of EMFAC, referred to as
EMFAC2017. See 84 FR 41717 (August 15, 2019). For the 2016 Ventura
County Ozone SIP, EMFAC2014 was the appropriate model to use for SIP
development purposes at the time it was prepared.
Table 5--Transportation Conformity Budgets for the 2008 Ozone NAAQS in
Ventura County
[Summer planning inventory, tpd]
------------------------------------------------------------------------
Budget year VOC NOX
------------------------------------------------------------------------
2020............................................ 5 7
------------------------------------------------------------------------
Source: 2016 Ventura County AQMP, Table 3-7, 52.
3. The EPA's Review of the State's Submission
As part of our review of the approvability of the budgets in the
2016 Ventura County AQMP, we have evaluated the budgets using our
adequacy criteria in 40 CFR 93.118(e)(4) and (5). We will complete the
adequacy review concurrent with our final action on the 2016 Ventura
County AQMP. The EPA is not required under its transportation
conformity rule to find budgets adequate prior to proposing approval of
them.\118\ Today, the EPA is announcing that the adequacy process for
these budgets begins, and the public has 30 days to comment on their
adequacy, per the transportation conformity regulation at 40 CFR
93.118(f)(2)(i) and (ii).
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\118\ Under the transportation conformity regulations, the EPA
may review the adequacy of submitted motor vehicle emission budgets
simultaneously with the EPA's approval or disapproval of the
submitted implementation plan. 40 CFR 93.118(f)(2).
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As documented in a separate memorandum included in the docket for
this rulemaking, we preliminarily conclude that the budgets in the 2016
Ventura County AQMP meet each adequacy criterion.\119\ While adequacy
and approval are two separate actions, reviewing the budgets in terms
of the adequacy criteria informs the EPA's decision to propose to
approve the budgets. We have completed our detailed review of the 2016
Ventura County AQMP and are proposing herein to approve the attainment
and RFP demonstrations. We have also reviewed the budgets in the 2016
Ventura County AQMP and found that they are consistent with the
attainment and RFP demonstrations for which we are proposing approval,
are based on control measures that have already been adopted and
implemented, and meet all other applicable statutory and regulatory
requirements including the adequacy criteria in 40 CFR 93.1118(e)(4)
and (5). Therefore, we are proposing to approve the 2020 budgets in the
2016 Ventura County AQMP. At the point when we either finalize the
adequacy process or approve the budgets for the 2008 ozone NAAQS in the
2016 Ventura County AQMP as proposed (whichever occurs first; note that
they could also occur concurrently per 40 CFR 93.118(f)(2)(iii)), they
will replace the budgets that we previously found adequate for use in
transportation conformity determinations.\120\
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\119\ Memorandum dated September 5, 2019, from John J. Kelly,
Air Planning Office, EPA Region 9, to docket for this proposed
rulemaking, titled ``Adequacy Documentation for Plan Motor Vehicle
Emission Budgets in 2016 Ventura County Ozone Plan.''
\120\ In May 2008, we found adequate the 2009 budgets from the
Ventura County 2008 8-hour Ozone Early Progress Plan (February
2008). 73 FR 24595 (May 5, 2008). The 2009 budgets are 13 tpd for
VOC and 19 tpd for NOX.
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Under our transportation conformity rule, as a general matter, once
budgets are approved, they cannot be superseded by revised budgets
submitted for the same CAA purpose and the same year(s) addressed by
the previously approved SIP until the EPA approves the revised budgets
as a SIP revision. In other words, as a general matter, such approved
budgets cannot be superseded by revised budgets found adequate, but
rather only through approval of the revised budgets, unless the EPA
specifies otherwise in its approval of a SIP by limiting the duration
of the approval to last only until subsequently submitted budgets are
found adequate.\121\
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\121\ 40 CFR 93.118(e)(1).
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In this instance, as noted above, in its submittal letter, CARB
requested that we limit the duration of our approval of the budgets in
the 2016 Ventura County AQMP only until the effective date of the EPA's
adequacy finding for subsequently submitted budgets, and in August
2019, CARB provided further explanation for its request. Generally, we
will consider a state's request to limit an approval of a budget only
if the request includes the following elements: \122\
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\122\ 67 FR 69139 (November 15, 2002) (final action limiting our
prior approval of budgets in certain California SIPs).
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An acknowledgement and explanation as to why the budgets
under consideration have become outdated or deficient;
A commitment to update the budgets as part of a
comprehensive SIP update; and
A request that the EPA limit the duration of its approval
to the time when new budgets have been found to be adequate for
transportation conformity purposes.
CARB's request includes an explanation for why the budgets have
become, or will become, outdated or deficient. In short, CARB requested
that
[[Page 70127]]
we limit the duration of the approval of the budgets in light of the
EPA's recent approval of EMFAC2017, an updated version of the model
(EMFAC2014) used for the budgets in the 2016 Ventura County AQMP.
EMFAC2017 updates vehicle mix and emissions data of the previously
approved version of the model, EMFAC2014.
Preliminary calculations by CARB indicate that EMFAC2017-derived
motor vehicle emissions estimates for Ventura County will exceed the
corresponding EMFAC2014-derived budgets in the 2016 Ventura County
AQMP. In light of the approval of EMFAC2017, CARB explains that the
budgets from the 2016 Ventura County AQMP, for which we are proposing
approval in today's action, will become outdated and will need to be
revised using EMFAC2017. In addition, CARB states that, without the
ability to replace the budgets using the budget adequacy process, the
benefits of using the updated data may not be realized for a year or
more after the updated SIP (with the EMFAC2017-derived budgets) is
submitted, due to the length of the SIP approval process. We find that
CARB's explanation for limiting the duration of the approval of the
budgets is appropriate and provides us with a reasonable basis on which
to limit the duration of the approval of the budgets.
We note that CARB has not committed to update the budgets as part
of a comprehensive SIP update, but as a practical matter, CARB must
submit a SIP revision that includes updated demonstrations as well as
the updated budgets to meet the adequacy criteria in 40 CFR
93.118(e)(4); \123\ and thus, we do not need a specific commitment for
such a plan at this time. For the reasons provided above, and in light
of CARB's explanation for why the budgets will become outdated and
should be replaced upon an adequacy finding for updated budgets, we
propose to limit the duration of our approval of the budgets in the
2016 Ventura County AQMP until we find revised budgets based on
EMFAC2017 to be adequate.
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\123\ Under 40 CFR 93.118(e)(4), the EPA will not find a budget
in a submitted SIP to be adequate unless, among other criteria, the
budgets, when considered together with all other emissions sources,
are consistent with applicable requirements for RFP and attainment.
40 CFR 93.118(e)(4)(iv).
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H. General Conformity Budgets
1. Statutory and Regulatory Requirements
Section 176(c) of the CAA requires federal actions in nonattainment
and maintenance areas to conform to the SIP's goals of eliminating or
reducing the severity and number of violations of the NAAQS and
achieving timely attainment of the standards. Conformity to the SIP's
goals means that such actions will not: (1) Cause or contribute to
violations of a NAAQS, (2) worsen the severity of an existing
violation, or (3) delay timely attainment of any NAAQS or any interim
milestone.
Section 176(c)(4) of the CAA establishes the framework for general
conformity. The EPA first promulgated general conformity regulations in
November 1993.\124\ On April 5, 2010, the EPA revised the general
conformity regulations.\125\ The general conformity regulations ensure
that federal actions not covered by the transportation conformity rule
will not interfere with the SIP and encourage consultation between the
federal agency and the state or local air pollution control agencies
before or during the environmental review process, as well as public
participation (e.g., notification of and access to federal agency
conformity determinations and review of individual federal actions).
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\124\ 40 CFR part 51, subpart W, and 40 CFR part 93, subpart B.
\125\ 75 FR 17254.
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The general conformity regulations provide three phases:
Applicability analysis, conformity determination, and review process.
The applicability analysis phase under 40 CFR 93.153 is used to find if
a federal action requires a conformity determination for a specific
pollutant. If a conformity determination is needed, federal agencies
can use one of several methods to show that the federal action conforms
to the SIP. In an area without a SIP, a federal action may be shown to
``conform'' by demonstrating there will be no net increase in emissions
in the nonattainment or maintenance area from the federal action. In an
area with a SIP, conformity to the applicable SIP can be demonstrated
in one of several ways. For actions where the direct and indirect
emissions exceed the rates in 40 CFR 93.153(b), the federal action can
include mitigation measures to offset the emission increases from the
federal action or can show that the action will conform by meeting any
of the following requirements:
Showing that the net emission increases caused by an
action are included in the SIP,
documenting that the state agrees to include the emission
increases in the SIP,
offsetting the action's emissions in the same or nearby
area of equal or greater classification, or
providing an air quality modeling demonstration in some
circumstances.\126\
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\126\ 40 CFR 93.158; and VCAPCD Rule 220 (``General
Conformity''), approved at 64 FR 19916 (April 23, 1999).
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The general conformity regulations at 40 CFR 93.161 allow state and
local air quality agencies working with federal agencies with large
facilities (e.g., commercial airports, ports, and large military bases)
that are subject to the general conformity regulations to develop and
adopt an emissions budget for those facilities in order to facilitate
future conformity determinations. Such a budget, referred to as a
facility-wide emissions budget, may be used by federal agencies to
demonstrate conformity as long as the total facility-wide budget level
identified in the SIP is not exceeded.
According to 40 CFR 93.161, the state or local agency responsible
for implementing and enforcing the SIP can develop and adopt an
emissions budget to be used for demonstrating conformity under 40 CFR
93.158(a)(1). The requirements include the following: (1) The facility-
wide budget must be for a set time period; (2) the budget must cover
the pollutants or precursors of the pollutants for which the area is
designated nonattainment or maintenance; (3) the budgets must be
specific about what can be emitted on an annual or seasonal basis; (4)
the emissions from the facility along with all other emissions in the
area must not exceed the total SIP emissions budget for the
nonattainment or maintenance area; (5) specific measures must be
included to ensure compliance with the facility-wide budget, such as
periodic reporting requirements or compliance demonstrations when the
federal agency is taking an action that would otherwise require a
conformity determination; (6) the budget must be submitted to the EPA
as a SIP revision; and (7) the SIP revision must be approved by the
EPA. Having or using a facility-wide emissions budget does not preclude
a federal agency from demonstrating conformity in any other manner
allowed by the conformity rule.
2. Summary of the State's Submission
The 2016 Ventura County AQMP establishes VOC and NOX
general conformity budgets for the Naval Base Ventura County (NBVC) for
each year from 2017 through 2020 as shown in Table 6 below. The budgets
are intended to reflect aircraft and missile operations associated with
NBVC Point Mugu and ship operations at Port Hueneme occuring within the
Ventura County
[[Page 70128]]
ozone nonattainment area. The budgets include a 4 percent growth
allowance to account for uncertainties in potential projects resulting
from future actions and unknown projects. As shown in Table 6, the
budgets for NBVC in the attainment year (2020) are 198.0 tpy of VOC and
475.9 tpy of NOX, which is equivalent to 0.54 tpd of VOC and
1.30 tpd of NOX on an annual average daily basis.
Table 6--NBVC General Conformity Budgets for the 2008 Ozone NAAQS in
Ventura County
[summer planning inventory, tpy]
------------------------------------------------------------------------
Budget year VOC NOX
------------------------------------------------------------------------
2017.............................................. 178.6 434.2
2018.............................................. 184.8 447.6
2019.............................................. 191.3 461.5
2020.............................................. 198.0 475.9
------------------------------------------------------------------------
Source: 2016 Ventura County Ozone AQMP, Table 4-9.
3. The EPA's Review of the State's Submission
We propose to approve the general conformity budgets in the 2016
Ventura County AQMP for NBVC shown in Table 6, as meeting the
requirements of CAA section 176(c) and 40 CFR 93.161. We find that the
general conformity budgets in the 2016 AQMP: are established for a set
time period; cover both precursors of ozone; are precisely quantified
in terms of tons per year; and, along with all other emissions in
Ventura County, are consistent with the RFP and attainment
demonstration for the 2008 ozone NAAQS.
If we finalize our approval of these budgets, NBVC can use these
budgets to demonstrate that their projects conform to the SIP through a
letter from the State and District confirming that the project
emissions are accounted for in the SIP's general conformity budgets.
I. Other Clean Air Act Requirements Applicable to Serious Ozone
Nonattainment Areas
In addition to the SIP requirements discussed in the previous
sections, the CAA includes certain other SIP requirements applicable to
Serious ozone nonattainment areas, such as Ventura County. We describe
these provisions and their current status below.
1. Enhanced Vehicle Inspection and Maintenance Programs
Section 182(c)(3) of the CAA requires states with ozone
nonattainment areas classified under subpart 2 as Serious or above to
implement an enhanced motor vehicle I/M program in those areas. The
requirements for those programs are provided in CAA section 182(c)(3)
and 40 CFR part 51, subpart S.
Consistent with the 2008 Ozone SRR, no new I/M programs are
currently required for nonattainment areas for the 2008 ozone
NAAQS.\127\ The EPA previously approved California's I/M program in
Ventura County as meeting the requirements of the CAA and applicable
EPA regulations for enhanced I/M programs.\128\
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\127\ 2008 Ozone SRR, 80 FR 12264, at 12283 (March 6, 2015).
\128\ 75 FR 38023 (July 1, 2010).
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2. New Source Review Rules
Section 182(a)(2)(C) of the CAA requires states to develop SIP
revisions containing permit programs for each of its ozone
nonattainment areas. The SIP revisions are to include requirements for
permits in accordance with CAA sections 172(c)(5) and 173 for the
construction and operation of each new or modified major stationary
source for VOC and NOX anywhere in the nonattainment area.
The 2008 Ozone SRR includes provisions and guidance for nonattainment
NSR programs.\129\ Earlier this year, the EPA proposed to approve the
nonattainment NSR SIP submitted for Ventura County for the 2008 ozone
NAAQS. The nonattainment NSR SIP includes a certification letter
documenting how the VCAPCD's SIP-approved nonattainment NSR program,
established in VCAPCD Rules 26 through 26.11, meets the applicable NSR
requirements for Ventura County for the 2008 ozone NAAQS.\130\ We
expect to take final action on the nonattainment NSR SIP for Ventura
County for the 2008 ozone NAAQS in the near future in a separate
rulemaking.
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\129\ 80 FR 12264 (March 6, 2015).
\130\ 84 FR 20604 (May 10, 2019); reproposed at 84 FR 43738
(August 22, 2019).
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3. Clean Fuels Fleet Program
Sections 182(c)(4)(A) and 246 of the CAA require California to
submit to the EPA for approval measures to implement a Clean Fuels
Fleet Program. Section 182(c)(4)(B) of the CAA allows states to opt-out
of the federal clean-fuel vehicle fleet program by submitting a SIP
revision consisting of a program or programs that will result in at
least equivalent long-term reductions in ozone precursors and toxic air
emissions.
In 1994, CARB submitted a SIP revision to the EPA to opt-out of the
federal clean-fuel fleet program. The submittal included a
demonstration that California's low-emissions vehicle program achieved
emissions reductions at least as large as would be achieved by the
federal program. The EPA approved the SIP revision to opt-out of the
federal program on August 27, 1999.\131\ There have been no changes to
the federal Clean Fuels Fleet program since the EPA approved the
California SIP revision to opt-out of the federal program, and no
corresponding changes to the SIP are required. Thus, we find that the
California SIP revision to opt-out of the federal program, as approved
in 1999, meets the requirements of CAA sections 182(c)(4)(A) and 246
for Ventura for the 2008 ozone NAAQS.
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\131\ 64 FR 46849 (August 27, 1999).
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4. Gasoline Vapor Recovery
Section 182(b)(3) of the CAA requires states to submit a SIP
revision by November 15, 1992, that requires owners or operators of
gasoline dispensing systems to install and operate gasoline vehicle
refueling vapor recovery (``Stage II'') systems in ozone nonattainment
areas classified as Moderate and above. California's ozone
nonattainment areas implemented Stage II vapor recovery well before the
passage of the CAA Amendments of 1990.\132\
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\132\ General Preamble, 57 FR 13498 at 13514 (April 16, 1992).
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Section 202(a)(6) of the CAA requires the EPA to promulgate
standards requiring motor vehicles to be equipped with onboard
refueling vapor recovery (ORVR) systems. The EPA promulgated the first
set of ORVR system regulations in 1994 for phased implementation on
vehicle manufacturers, and since the end of 2006, essentially all new
gasoline-powered light- and medium-duty vehicles are ORVR-
equipped.\133\ Section 202(a)(6) also authorizes the EPA to waive the
SIP requirement under CAA section 182(b)(3) for installation of Stage
II vapor recovery systems after such time as the EPA determines that
ORVR systems are in widespread use throughout the motor vehicle fleet.
Effective May 16, 2012, the EPA waived the requirement of CAA section
182(b)(3) for Stage II vapor recovery systems in ozone nonattainment
areas regardless of classification.\134\ Thus, a SIP submittal meeting
CAA section 182(b)(3) is not required for the 2008 ozone NAAQS.
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\133\ 77 FR 28772, at 28774 (May 16, 2012).
\134\ See 40 CFR 51.126(b).
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While a SIP submittal meeting CAA section 182(b)(3) is not required
for the 2008 ozone NAAQS, under California state law (i.e., Health and
Safety Code section 41954), CARB is required to adopt procedures and
performance standards for controlling gasoline emissions from gasoline
marketing
[[Page 70129]]
operations, including transfer and storage operations. State law also
authorizes CARB, in cooperation with local air districts, to certify
vapor recovery systems, to identify defective equipment and to develop
test methods. CARB has adopted numerous revisions to its vapor recovery
program regulations and continues to rely on its vapor recovery program
to achieve emissions reductions in ozone nonattainment areas in
California.
In Ventura County, the installation and operation of CARB-certified
vapor recovery equipment is required and enforced through VCAPCD Rule
70 (``Storage And Transfer Of Gasoline''), which was most recently
approved into the SIP on January 31, 2011.\135\
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\135\ 76 FR 5277 (January 31, 2011). See also, 69 FR 29451 (May
24, 2004) (The EPA's approval of an earlier version of VCAPCD Rule
70 as meeting the requirements of CAA section 182(b)(3)).
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5. Enhanced Ambient Air Monitoring
Section 182(c)(1) of the CAA requires that all ozone nonattainment
areas classified as Serious or above implement measures to enhance and
improve monitoring for ambient concentrations of ozone, NOX,
and VOC, and to improve monitoring of emissions of NOX and
VOC. The enhanced monitoring network for ozone is referred to as the
photochemical assessment monitoring station (PAMS) network. The EPA
promulgated final PAMS regulations on February 12, 1993.\136\
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\136\ 58 FR 8452 (February 12, 1993).
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On November 10, 1993, CARB submitted to the EPA a SIP revision
addressing the PAMS network for six ozone nonattainment areas in
California, including Ventura County, to meet the enhanced monitoring
requirements of CAA section 182(c)(1) and the PAMS regulations. The EPA
determined that the PAMS SIP revision met all applicable requirements
for enhanced monitoring and approved the PAMS submittal into the
California SIP.\137\
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\137\ 82 FR 45191 (September 28, 2017).
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Prior to 2006, the EPA's ambient air monitoring regulations in 40
CFR part 58 (``Ambient Air Quality Surveillance'') set forth specific
SIP requirements (see former 40 CFR 52.20). In 2006, the EPA
significantly revised and reorganized 40 CFR part 58.\138\ Under
revised 40 CFR part 58, SIP revisions are no longer required; rather,
compliance with EPA monitoring regulations is established through
review of required annual monitoring network plans.\139\ The 2008 Ozone
SRR made no changes to these requirements.\140\
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\138\ 71 FR 61236 (October 17, 2006).
\139\ 40 CFR 58.2(b) now provides that, ``The requirements
pertaining to provisions for an air quality surveillance system in
the SIP are contained in this part.''
\140\ The 2008 ozone SRR addresses PAMS-related requirements at
80 FR 12264, at 12291 (March 6, 2015).
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The 2016 Ventura County Ozone SIP does not specifically address the
enhanced ambient air monitoring requirement in CAA section 182(c)(1).
However, we note that CARB includes the ambient monitoring network
within Ventura County in its annual monitoring network plan that is
submitted to the EPA, and that we have approved the most recent annual
monitoring network plan (``Annual Network Plan Covering Monitoring
Operations in 25 California Air Districts (June 2018)'' or ``2018
ANP'') with respect to the Ventura County element.\141\ Based on our
review and approval of the 2018 ANP with respect to Ventura County and
our earlier approval of the PAMS SIP revision, we propose to find that
CARB and VCAPCD meet the enhanced monitoring requirements under CAA
section 182(c)(1) for Ventura County with respect to the 2008 ozone
NAAQS.
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\141\ Letter dated November 26, 2018, from Gwen Yoshimura,
Manager, Air Quality Analysis Office, EPA Region IX, to Ravi
Ramalingam, Chief, Consumer Products and Air Quality Assessment
Branch, Air Quality Planning and Science Division, CARB.
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IV. Proposed Action
For the reasons discussed in this notice, under CAA section
110(k)(3), the EPA is proposing to approve as a revision to the
California SIP the following portions of the 2016 Ventura County Ozone
SIP submitted by CARB on April 11, 2017 and December 5, 2018:
Base year emissions inventory element in the 2016 Ventura
County AQMP as meeting the requirements of CAA sections 172(c)(3) and
182(a)(1) and 40 CFR 51.1115 for the 2008 ozone NAAQS;
Emissions statement element in the 2016 Ventura County
AQMP as meeting the requirements of CAA section 182(a)(3)(B) and 40 CFR
51.1102 for the 2008 ozone NAAQS;
RACM demonstration element in the 2016 Ventura County AQMP
as meeting the requirements of CAA section 172(c)(1) and 40 CFR
51.1112(c) for the 2008 ozone NAAQS;
Attainment demonstration element for the 2008 ozone NAAQS
in the 2016 Ventura County AQMP as meeting the requirements of CAA
section 182(c)(2)(A) and 40 CFR 51.1108;
ROP demonstration element in the 2016 Ventura County AQMP
as meeting the requirements of CAA 182(b)(1) and 40 CFR 51.1110(a)(2)
for the 2008 ozone NAAQS;
RFP demonstration element in the 2018 SIP Update, as
clarified in August 2019,\142\ as meeting the requirements of CAA
sections 172(c)(2) and 182(c)(2)(B), and 40 CFR 51.1110(a)(2)(ii) for
the 2008 ozone NAAQS;
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\142\ Letter dated August 29, 2019, from Dr. Michael T.
Benjamin, Chief, Air Quality Planning and Science Division, CARB, to
Amy Zimpfer, Assistant Director, Air Division, EPA Region IX.
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Motor vehicle emissions budgets in the 2016 Ventura County
AQMP for the RFP milestone/attainment year of 2020 (as shown in Table
5) because they are consistent with the RFP and attainment
demonstrations for the 2008 ozone NAAQS proposed for approval herein
and meet the other criteria in 40 CFR 93.118(e); and
General conformity budgets of VOC and NOX (as
shown in Table 6) for Naval Base Ventura County, as meeting the
requirements of CAA section 176(c) and 40 CFR 93.161.
We are also proposing to find that the:
Enhanced vehicle inspection and maintenance program in
Ventura County meets the requirements of CAA section 182(c)(3) and 40
CFR 51.1102 for the 2008 ozone NAAQS;
California SIP revision to opt-out of the federal Clean
Fuels Fleet Program meets the requirements of CAA sections 182(c)(4)(A)
and 246 and 40 CFR 51.1102 for the 2008 ozone NAAQS with respect to
Ventura County; and
Enhanced monitoring in Ventura County meets the
requirements of CAA section 182(c)(1) and 40 CFR 51.1102 for the 2008
ozone NAAQS.\143\
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\143\ Regarding other applicable requirements for the 2008 ozone
NAAQS in Ventura County, the EPA has previously approved SIP
revisions that address the nonattainment area requirements for
implementation of RACT for Ventura County for the 2008 ozone NAAQS.
See 80 FR 2016 (January 15, 2015) (approval of Ventura County RACT
SIP). With respect to the Nonattainment NSR SIP for Ventura County
for the 2008 ozone NAAQS, the EPA proposed approval at 84 FR 20604
(May 10, 2019) and is expected to take final action in the near
future.
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With respect to the motor vehicle emissions budgets, we are
proposing to limit the duration of the approval of the budgets to last
only until the effective date of the EPA's adequacy finding for any
subsequently submitted budgets. We are doing so at CARB's request and
in light of the benefits of using EMFAC2017-derived budgets prior to
our taking final action on the future SIP revision that includes the
updated budgets.
In addition, we are proposing, under CAA section 110(k)(4), to
approve conditionally the contingency measure element of the 2016
Ventura County Ozone SIP as meeting the requirements
[[Page 70130]]
of CAA sections 172(c)(9) and 182(c)(9) for RFP and attainment
contingency measures. Our proposed approval is based on commitments by
the District and CARB to supplement the element through submission, as
a SIP revision (within one year of the effective date of our final
conditional approval action), of a revised District rule or rules that
would add new limits or other requirements if an RFP milestone is not
met or if Ventura County fails to attain the 2008 ozone NAAQS by the
applicable attainment date.\144\
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\144\ Letter dated August 16, 2019, from Michael Villegas, Air
Pollution Control Officer, VCAPCD, to Richard Corey, Executive
Officer, CARB; and letter dated August 30, 2019, from Richard W.
Corey, Executive Officer, CARB, to Mike Stoker, Regional
Administrator, EPA Region IX.
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The EPA is soliciting public comments on the issues discussed in
this document. We will accept comments from the public on this proposal
for the next 30 days and will consider comments before taking final
action.
V. Statutory and Executive Order Reviews
Under the Clean Air Act, the Administrator is required to approve a
SIP submission that complies with the provisions of the Act and
applicable federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions, the EPA's role is to approve state
choices, provided that they meet the criteria of the Clean Air Act.
Accordingly, this proposed action merely proposes to approve, or
conditionally approve, state plans as meeting federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this proposed action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
Is not an Executive Order 13771 (82 FR 9339, February 2,
2017) regulatory action because SIP approvals are exempted under
Executive Order 12866;
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
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);
Does not have Federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of Section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the Clean Air Act; and
Does not provide the EPA with the discretionary authority
to address disproportionate human health or environmental effects with
practical, appropriate, and legally permissible methods under Executive
Order 12898 (59 FR 7629, February 16, 1994).
In addition, the SIP is not approved to apply on any Indian
reservation land or in any other area where the EPA or an Indian tribe
has demonstrated that a tribe has jurisdiction. In those areas of
Indian country, the proposed rule does not have tribal implications and
will not impose substantial direct costs on tribal governments or
preempt tribal law as specified by Executive Order 13175 (65 FR 67249,
November 9, 2000).
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Intergovernmental relations, Nitrogen dioxide, Ozone,
Reporting and recordkeeping requirements, Volatile organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 5, 2019.
Michael Stoker,
Regional Administrator, Region IX.
[FR Doc. 2019-27545 Filed 12-19-19; 8:45 am]
BILLING CODE 6560-50-P