Approval and Promulgation of Implementation Plans; California; Revisions to the California State Implementation Plan Pesticide Element, 24441-24451 [2012-9850]
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Federal Register / Vol. 77, No. 79 / Tuesday, April 24, 2012 / Proposed Rules
Region 4, 61 Forsyth Street SW.,
Atlanta, Georgia 30303–8960.
5. Hand Delivery or Courier: Lynorae
Benjamin, Regulatory Development
Section, Air Planning Branch, Air,
Pesticides and Toxics Management
Division, U.S. Environmental Protection
Agency, Region 4, 61 Forsyth Street
SW., Atlanta, Georgia 30303–8960. Such
deliveries are only accepted during the
Regional Office’s normal hours of
operation. The Regional Office’s official
hours of business are Monday through
Friday, 8:30 a.m. to 4:30 p.m., excluding
federal holidays.
Please see the direct final rule which
is located in the Rules section of this
Federal Register for detailed
instructions on how to submit
comments.
Sara
Waterson, Regulatory Development
Section, Air Planning Branch, Air,
Pesticides and Toxics Management
Division, U.S. Environmental Protection
Agency, Region 4, 61 Forsyth Street
SW., Atlanta, Georgia 30303–8960. The
telephone number is (404) 562–9061.
Ms. Waterson can be reached via
electronic mail at
waterson.sara@epa.gov.
FOR FURTHER INFORMATION CONTACT:
On March
12, 2008, EPA issued a revised ozone
NAAQS. See 73 FR 16436. The current
action, however, is being taken to
address requirements under the 1997 8hour ozone NAAQS. Requirements for
the Atlanta Area under the 2008 ozone
NAAQS will be addressed in the future.
For additional information see the direct
final rule which is published in the
Rules Section of this Federal Register.
A detailed rationale for the approval is
set forth in the direct final rule. If no
adverse comments are received in
response to this rule, no further activity
is contemplated. If EPA receives adverse
comments, the direct final rule will be
withdrawn and all public comments
received will be addressed in a
subsequent final rule based on this
proposed rule. EPA will not institute a
second comment period on this
document. Any parties interested in
commenting on this document should
do so at this time.
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SUPPLEMENTARY INFORMATION:
Dated: April 4, 2012.
A. Stanley Meiburg,
Acting Regional Administrator, Region 4.
[FR Doc. 2012–9706 Filed 4–23–12; 8:45 am]
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R09–OAR–2012–0194; FRL–9664–5]
Approval and Promulgation of
Implementation Plans; California;
Revisions to the California State
Implementation Plan Pesticide Element
U.S. Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
EPA proposes to approve
several revisions to the Pesticide
Element of the California state
implementation plan (SIP). These
revisions include regulations adopted
by the California Department of
Pesticide Regulation (CDPR) that: (1)
Reduce volatile organic compound
(VOC) emissions from the application of
agricultural field fumigants in the South
Coast, Southeast Desert, Ventura, San
Joaquin Valley (SJV), and Sacramento
Metro ozone nonattainment areas by
restricting fumigant application
methods; (2) establish a contingency
fumigant emissions limit and allocation
system for Ventura; (3) require CDPR to
prepare and make available to the
public an annual pesticide VOC
emissions inventory report; and (4)
require recordkeeping and reporting of
pesticide usage. EPA also proposes to
approve CDPR’s commitments to
manage VOC emissions from the use of
agricultural and commercial structural
pesticides in the SJV to ensure that they
do not exceed 18.1 tons per day and to
implement restrictions on VOC
emissions in the SJV from non-fumigant
pesticides by 2014. Lastly, EPA is
providing its response to a remand by
the Ninth Circuit Court of Appeals of
EPA’s 2009 approval of a revision to the
California SIP related to reducing VOC
emissions from pesticides.
DATES: Any comments must arrive by
May 24, 2012.
ADDRESSES: Submit comments,
identified by docket number EPA–R09–
OAR–2012–0194, by one of the
following methods:
• Federal eRulemaking Portal:
www.regulations.gov. Follow the on-line
instructions.
• Email: steckel.andrew@epa.gov.
• Mail or deliver: Andrew Steckel,
(AIR–4), U.S. Environmental Protection
Agency Region 9, 75 Hawthorne Street,
San Francisco, CA 94105.
Instructions: All comments will be
included in the public docket without
change and may be made available
online at www.regulations.gov,
SUMMARY:
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including any personal information
provided, unless the comment includes
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Information that
you consider CBI or otherwise protected
should be clearly identified as such and
should not be submitted through
www.regulations.gov or email. The
www.regulations.gov Web site is an
‘‘anonymous access’’ system, and EPA
will not know your identity or contact
information unless you provide it in the
body of your comment. If you send
email directly to EPA, your email
address will be automatically captured
and included as part of the public
comment. If EPA cannot read your
comments due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment.
Docket: The technical support
document (TSD) and the index to the
docket for this proposed action is
available electronically on the
www.regulations.gov Web site and in
hard copy at EPA Region 9, 75
Hawthorne Street, San Francisco,
California 94105. While all documents
in the docket are listed in the index,
some information may be publicly
available only at the hard copy location
(e.g., copyrighted material), and some
may not be publicly available at either
location (e.g., CBI). To inspect the hard
copy materials, please schedule an
appointment during normal business
hours with either of the contacts listed
in the FOR FURTHER INFORMATION
CONTACT section below.
FOR FURTHER INFORMATION CONTACT: For
information on the proposed action on
CDPR’s regulations: Nancy Levin, Rules
Office (AIR–4), (415) 972–3848,
levin.nancy@epa.gov. For information
on the proposed actions on CDPR’s
commitments and the PEST–1 measure:
Frances Wicher, Air Planning Office
(AIR–2), (415) 972–3957,
wicher.frances@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we’’, ‘‘us’’
and ‘‘our’’ refer to EPA.
Table of Contents
I. Introduction
II. The Current California SIP Pesticide
Element and Description of the Proposed
Revisions
A. Currently-Approved Provisions of the
California SIP Pesticide Element
B. Proposed Revisions to the California SIP
Pesticide Element
III. EPA’s Evaluation of the Revisions to the
California SIP Pesticide Element
A. Clean Air Act (CAA) Procedural and
Administrative Requirements for SIP
Submittals Under CAA Section 110
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B. Enforceability of Emission Limitations
Under CAA Section 110(a)(2)(A)
C. Reasonably Available Control Measures/
Reasonably Available Control
Technology (RACM/RACT) Requirement
Under CAA Sections 172(c)(1) and
182(b)(1)
D. Finding of Non-Interference With
Applicable Requirements of the CAA
Under Section 110(l)
IV. Response To Remand in Association of
Irritated Residents Case
V. Proposed Actions and Opportunity for
Public Comment
VI. Statutory and Executive Order Reviews
I. Introduction
This proposed action deals with
revisions to California’s federallyapproved program to reduce emissions
from the use of agricultural and
structural pesticides to improve ozone
air quality in five areas of the State: the
South Coast, Southeast Desert (SED),
Ventura, San Joaquin Valley (SJV), and
Sacramento Metro nonattainment areas.
Pesticides contribute to ozone pollution
through the emissions of volatile
organic compounds (VOC). VOC react in
the atmosphere with nitrogen oxides
(NOX) in the presence of sunlight to
form ozone. Breathing ground-level
ozone can result in a number of health
effects that are observed in broad
segments of the population. These
health effects include reduced lung
function and inflamed airways, which
can increase respiratory symptoms and
aggravate asthma or other lung diseases.
Ozone exposure also has been
associated with increased susceptibility
to respiratory infections, medication
use, doctor visits, and emergency
department visits and hospital
admissions for individuals with lung
disease. Ozone exposure also increases
the risk of premature death from heart
or lung disease. Children are at
increased risk from exposure to ozone
because their lungs are still developing
and they are more likely to be active
outdoors, which increases their
exposure.
Pesticides contribute about 5 percent
to total VOC emissions in SJV and
Ventura ozone nonattainment areas and
less than 1 percent to total VOC
emissions in the South Coast, SED, and
Sacramento Metro areas. See TSD,
section I.D.
This proposal addresses the
regulation of VOC emissions from
pesticides under the federal Clean Air
Act (CAA or ‘‘Act’’). Pesticides and their
uses and application are primarily
regulated under Federal Insecticide,
Fungicide, and Rodenticide Act
(FIFRA). This proposal does not address
regulations of pesticides under FIFRA or
other federal acts.
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II. The Current California SIP Pesticide
Element and a Description of the
Proposed Revisions
A. Currently-Approved Provisions of the
California SIP Pesticide Element
Prior to today’s proposal, EPA has
taken three actions to either approve or
revise provisions of the California SIP
Pesticide Element. We briefly describe
each action below. More information on
each action and its background can be
found in section I.E. of the TSD for this
proposal.
• 1994 Pesticide Element—The 1994
Pesticide Element was submitted by
California in November 1994 as part of
the State’s comprehensive 1-hour ozone
attainment plan (known as the 1994
Ozone SIP) and included a plan by
CDPR to reduce VOC emissions from
agricultural and structural pesticides in
five ozone nonattainment areas by a
maximum of 20 percent from 1990
baseline levels by 2005 and to adopt
regulations if necessary to achieve these
reductions. EPA approved the 1994
Pesticide Element on January 8, 1997
(62 FR 1150) and codified it at 40 CFR
52.220(c)(204)(i)(A)(6) and
52.220(c)(236).
• PEST–1 Measure in CARB’s 2003
State Strategy—In 2003, the California
Air Resources Board (CARB) updated
the statewide strategy that was part of
the 1994 Ozone SIP. One of the
measures in the 2003 State Strategy was
PEST–1 (‘‘Implement Existing Pesticide
Strategy’’), which retained and
continued unchanged the provisions of
the 1994 Pesticide Element. EPA
approved the PEST–1 measure into the
California SIP as part of its action to
approve in part and disapprove in part
the 2003 South Coast Air Quality
Management Plan and 2003 State
Strategy. See 74 FR 10176 (March 10,
2009), codified at 40 CFR
52.220(c)(339)(ii)(A)(1).1
• 2007 Ventura Pesticide Element—In
2007, CARB submitted a revision to the
Ventura portion of the 1994 Pesticide
Element. This revision reduced in part
and temporally the emissions reduction
commitment for Ventura in 1994
Pesticide Element. EPA approved this
revision in 2008. See 73 FR 41277 (July
18, 2008), codified at 40 CFR
52.220(c)(355)(i)(A).
1 In Association of Irritated Residents v. EPA, No.
09–71383, the 9th Circuit Court of Appeals
remanded the approval of PEST–1 to EPA with the
instructions to determine whether the Pesticide
Element has sufficient enforcement mechanisms to
satisfy the requirements of the Clean Air Act (CAA
or Act). We provide our response to the remand in
section IV of this notice.
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B. Proposed Revisions to the California
SIP Pesticide Element
EPA is proposing to approve
regulations and commitments adopted
by the CDPR to limit VOC emissions
from the use of agricultural and
commercial structural pesticides in the
South Coast, SED, Ventura, SJV, and
Sacramento Metro ozone nonattainment
areas.2 These CDPR regulations and
commitments were submitted by CARB
to EPA as follows:
1. October 12, 2009 submittal 3 of the
following CDPR regulations:
• Title 3 California Code of
Regulations (CCR), sections 6447 (first
paragraph) and 6447.3–6452 pertaining
to field fumigation methods;
• Portions of 3 CCR sections 6452.1–
6452.4 and sections 6624–6626
pertaining to emission inventory;
• 3 CCR sections 6452.2 and 6452.3
pertaining to field fumigation limits and
allowances in the Ventura ozone
nonattainment area.4
2. October 12, 2009 submittal 5 of
CDPR’s revised ‘‘Pesticide Emission
Reduction Commitment for the San
Joaquin Valley’’. This submittal caps
VOC emissions from the use of
agricultural and commercial structural
pesticides in the SJV to 18.1 tpd and
commits CDPR to implement
restrictions on non-fumigant pesticides
in the SJV by 2014.
3. August 2, 2011 submittal 6 of the
following CDPR regulations which
revised in part and added to the October
12, 2009 submittal: 7
2 The South Coast nonattainment area includes
Orange County and portions of Los Angeles, San
Bernardino, and Riverside Counties. The Southeast
Desert (SED) nonattainment area includes the
Coachella Valley in Riverside County, Antelope
Valley in Los Angeles County, and the
southwestern quadrant of San Bernardino County.
The Ventura nonattainment area is Ventura County.
The San Joaquin Valley (SJV) nonattainment area
includes San Joaquin, Stanislaus, Merced, Madera,
Fresno, Tulare and Kings Counties and the valley
portion of Kern County. The Sacramento Metro
nonattainment area includes Sacramento County
and parts of El Dorado, Placer, Solano and Sutter
Counties.
3 See letter, James N. Goldstene, Executive
Officer, CARB to Laura Yoshii, Acting Regional
Administrator, EPA Region 9, October 12, 2009.
4 CARB did not submit for inclusion into the SIP
those portions of 3 CCR sections 6452.2 and 6452.3
pertaining to field fumigation limits and allowances
in the South Coast, SED, SJV, and Sacramento
Metro ozone nonattainment areas.
5 See letter, James N. Goldstene, Executive
Officer, CARB to Laura Yoshii, Acting Regional
Administrator, EPA Region 9, October 12, 2009.
6 See letter, James N. Goldstene, Executive
Officer, CARB to Jared Blumenfeld, Regional
Administrator, EPA Region 9, August 2, 2011.
7 As part of its August 2, 2011 submittal, CARB
also submitted 3 CCR section 6400 (Restricted
Materials), 6446 (Methyl Iodide Field—General
Requirements) and section 6446.1 (Methyl Iodide
Field Fumigation Methods) and methyl-iodide
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• 3 CCR sections 6448.1, 6449.1, and
6450.1 pertaining to fumigation method
restrictions.
• Portions of 3 CCR sections 6452.2
and 6452.3 pertaining to field
fumigation limits and allowances in the
Ventura ozone nonattainment area.
• 3 CCR section 6452.4 pertaining to
the annual VOC emissions inventory
report.
• 3 CCR sections 6624 and 6626
pertaining to pesticide use records and
reports.
The submitted CDPR regulations that
we are proposing action on today can be
divided into four distinct but related
parts. The first part (3 CCR sections
6447 through 6452) establishes
standards for fumigant application and
restricts the use of certain higheremitting application methods in the five
nonattainment areas. The second part (3
CCR sections 6452.2 and 6452.3)
provides a contingency mechanism to
limit VOC emissions from field
fumigant applications in the Ventura
nonattainment area. The third part (3
CCR section 6452.4) requires CDPR to
annually report on pesticide VOC
emissions in each of the five
nonattainment areas and establishes
requirements for the report. The fourth
part (3 CCR sections 6624 and 6626)
establishes the recordkeeping and
reporting requirements necessary to
ensure compliance with the other parts.
We describe each part in more detail
below.
The first part (3 CCR sections 6447
through 6452) establishes, by fumigant
and method, requirements for the field
application of seven fumigants and
restricts the use of certain higheremitting application methods in the
South Coast, SED, Ventura, SJV, and
Sacramento Metro ozone nonattainment
areas during the period May 1 to
October 31.8 Requirements are
described for the field fumigants:
methyl bromide (sections 6447 and
6447.3), 1,3-dichloropropene (sections
6448 and 6448.1), chloropicrin (sections
6449 and 6449.1), metam-sodium,
potassium N-methyldithiocarbamate
related portions of provisions 6452.2(a)(4)(Annual
Volatile Organic Compound Emissions Inventory
Report) and 6624(f) (Pesticide Use Records). We are
deferring action on these provisions due to
California’s cancellation, effective March 21, 2012,
of the registration of all products containing the
active ingredient methyl iodide. CDPR adopted this
set of methyl iodide-related regulations on May 11,
2011, after and separately from the CDPR April 7,
2011 regulations that are also included in the CARB
August 2, 2011 submittal.
8 CDPR’s regulations establishing the parameters
for field fumigant application methods (but not the
restrictions on which methods may be used during
certain periods of the year) apply statewide;
however, EPA is limiting its approval to just the
five listed nonattainment areas.
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and dazomet (sections 6450, 6450.1 and
6450.2), and sodium tetrathiocarbonate
(sections 6451 and 6451.1).
Specific requirements for applying
these fumigants include, for example,
limiting fumigant application rates
(pounds/acre); specifying application
methods (e.g., minimum injection depth
below soil surface, number of water
treatments, minimum hours to leave
tarpaulin in place); and requiring plans
to address damaged tarpaulins. 3 CCR
section 6452 allows CDPR to approve
alternative fumigation methods under
certain conditions and based on specific
criteria.
As submitted, the second part of
CDPR’s regulations (3 CCR sections
6452.2 and 6452.3) apply only to the
Ventura ozone nonattainment area. This
part requires CDPR to set a field
fumigant VOC emissions limit for
Ventura in its annual VOC emissions
inventory report if overall pesticide
emissions (not just fumigant emissions)
in the Ventura nonattainment area are
found to be within five percent of or
exceed the listed benchmark. The
benchmark is equivalent to the 20
percent reduction in pesticide VOC
emissions from 1990 emissions levels
that is required in the area by the
California SIP Pesticide Element. This
part further requires that the county
agricultural commissioner add
conditions to field fumigation permits
or take other actions that will prevent
the field fumigant limit from being
exceeded.
The third part of the submitted
regulations (3 CCR section 6452.4)
requires CDPR to issue an annual
emissions inventory report that reports
the total agricultural and commercial
structural (fumigant and nonfumigant)
pesticide VOC emissions for previous
years in each of the five nonattainment
areas and evaluates compliance with the
emissions reduction targets in each area.
This section specifies the method for
calculating emissions and requires
CDPR make a draft emissions inventory
available to the public for a 45-day
comment period and post the final
report on its Web site.
The fourth part of the submitted
regulations (3 CCR sections 6624 and
6626) establishes the pesticide use
recordkeeping and reporting
requirements needed to assure
compliance with the other parts. This
part requires anyone using pesticides in
specific applications to keep and
maintain certain records for two years
and requires operators of property that
produces an agricultural commodity
and agricultural pest control businesses
to report the use of pesticides to the
county agricultural commissioner.
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These sections require the recording and
reporting of the method for fumigant
application in the five nonattainment
areas.
CDPR has revised its commitments in
the 1994 Pesticide Element to limit VOC
emissions from agricultural and
commercial structural pesticides in the
SJV. Specifically, it is now committing
to
• Use a specified emissions
estimation methodology to establish the
1990 pesticide VOC emission levels and
evaluate compliance with the provisions
in the 1994 Pesticide Element for SJV;
• Implement restrictions on
agricultural fumigation methods and by
2014 implement restrictions on VOC
emissions from non-fumigant pesticides;
and
• Manage VOC emissions from
agricultural and commercial structural
pesticide use to ensure that they do not
exceed 18.1 tons-per-day in the SJV area
(which is equivalent to a 12 percent
reduction in pesticide VOC emissions
from 1990 levels).
III. EPA’s Evaluation of the Revisions to
the California SIP Pesticide Element
A. CAA Procedural and Administrative
Requirements for SIP Submittals Under
CAA Section 110
CAA sections 110(a)(1) and (2) and
110(l) require a state to provide
reasonable public notice and
opportunity for public hearing prior to
the adoption and submittal 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 EPA’s implementing regulations in
40 CFR 51.102. All three submittals
under consideration here included
evidence of adequate public notice and
opportunity for comment.
CAA section 110(k)(1)(B) requires
EPA to determine whether a SIP
submittal is complete within 60 days of
receipt. This section also provides that
any SIP submittal that we have not
affirmatively determined to be complete
or incomplete will become complete by
operation of law six months after the
day of submittal. The October 12, 2009
submittals of the CDPR’s regulations
and the revised SJV Pesticide Element
went complete by operation of law on
April 12, 2009. The August 2, 2011
submittal of revisions to CDPR’s
regulations went complete by operation
of law on February 2, 2012.
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B. Enforceability of Emission
Limitations Under CAA Section
110(a)(2)(A)
CAA section 110(a)(2)(A) requires that
SIP ‘‘shall include enforceable
emissions limitations, and such other
control measures, means or techniques
(* * *) as well as schedules and
timetables for compliance, as may be
necessary or appropriate for attainment
* * *.’’
In order to be enforceable, SIP
regulations and commitments must be
clear regarding, for example, who must
comply, by what date, the standard of
compliance, the methods used to
determine compliance, and the process
and criteria for obtaining any variation
from the normal mode of compliance.9
Guidance used to help evaluate
enforceability includes the Bluebook
and the Little Bluebook.10
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Field Fumigant Regulations
CDPR’s regulations include
recordkeeping requirements in 3 CCR
section 6624 (Pesticide Use Records)
and the reporting requirements in 3 CCR
section 6626 (Pesticide Use Reports for
Production Agriculture). Among these
recordkeeping and reporting
requirements is the provision that
require any person who uses a fumigant
in any of the five ozone nonattainment
areas to record and report a description
of the application method. See 3 CCR
sections 6624(f) and 6626(d). The
regulations provide specific methods,
limits, and timeframes for agricultural
use of each fumigant. The regulations
provide a process and criteria for use of
a field fumigation method not described
in the regulations. The request to
implement a method not described in
the regulations must be accompanied by
scientific data documenting the VOC
emissions, and that the method will not
result in emissions greater than any one
of the methods allowed for use by the
regulations. The director must consider
criteria such as data sufficiency and
validity, and representativeness of field
conditions studied. See 3 CCR section
6452.
9 ‘‘Review of State Implementations Plans and
Revisions for Enforceability and Legal Sufficiency’’
(Enforceability Guidance), Craig Potter, EPA,
September 23, 1987. See also General Preamble for
the Implementation of Title I of the Clean Air Act
Amendments of 1990. 57 FR 13498, 13502 and
13541 (April 16, 1992) and CAA sections 110(a)(2)
and 172(c)(6). https://www.epa.gov/compliance/
resources/policies/civil/caa/stationary/review-enfrpt.pdf.
10 ‘‘Issues Relating to VOC Regulation Cutpoints,
Deficiencies, and Deviations,’’ U.S. EPA, OAQPS,
May 25, 1988 (‘‘the Bluebook’’) and ‘‘Guidance
Document for Correcting Common VOC and Other
Rule Deficiencies,’’ U.S. EPA Region 9, August 21,
2001 (‘‘the Little Bluebook’’).
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The recordkeeping and report
requirements and other rule provisions
in the submitted regulations are clear
and adequate to ensure that California’s
submitted fumigant regulations is
enforceable as required by of CAA
section 110(a)(2)(A).
Pesticide Emission Reduction
Commitment for the San Joaquin Valley
The mechanism to track compliance
with the 18.1 tpd limit on VOC
emissions from agricultural and
commercial structural pesticides in SJV
is the Annual VOC Emissions Inventory
Report required by 3 CCR section
6452.4. (Annual Volatile Organic
Compound Emissions Inventory
Report). For tracking compliance with
the overall VOC limit in the SJV, CDPR
proposes to use the emissions
estimation methodology described on
page 2–4 (in the section ‘‘Procedure for
Calculating Unadjusted and Adjusted
Volatile Organic Compound
Emissions’’) of November 5, 2008
memorandum from Rosemary Neal,
CDPR to Randy Segawa, CDPR, Subject:
Update to the Pesticide Volatile Organic
Inventory; Estimated Emissions 1990–
2006, and Preliminary Estimates for
2007 (‘‘Neal memorandum’’).11
Procedures for calculating pesticide
VOC emissions are also in 3 CCR section
6452.4(a)(1).12 The Neal memorandum
lays out a calculation process that
follows standard inventorying practice
and provides the same procedures for
calculating VOC emissions as 3 CCR
section 6452.4(a)(1). Pesticide usage
rates used to calculate total emissions
are collected from pesticide use reports
which are required by 3 CCR section
6626 and the requirements for persons
(e.g., pesticide applicators) to keep and
report the data necessary for preparing
the annual report are in 3 CCR section
6624. These provisions are clear and
adequate in combination with the
fumigant regulations to ensure the
pesticide VOC limit for the SJV is
enforceable as required by CAA section
110(a)(2)(A).
CDPR has committed to implement
restrictions on VOC emissions from
non-fumigant regulations by 2014 which
we interpret to mean by no later than
May 1, 2014 given that CDPR projects
emissions reductions from these
restrictions in 2014 and its control
11 The Neal memorandum was included as part of
October 12, 2009 submittal of the ‘‘Pesticide
Emission Reduction Commitment for the San
Joaquin Valley’’ and we intend to include it as
additional material in the California SIP should we
finalize our proposed approval of CDPR’s
commitment.
12 These procedures apply not only to SJV but
also to the other four nonattainment areas.
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program operates from May 1 to October
31 of each year. See ‘‘Proposed SIP
Commitment for San Joaquin Valley,’’
page 2. To achieve reductions in 2014,
the restriction would need to be
implemented by the beginning of the
regulatory season (May 1) in that year.
CDPR does not commit to a specific
emissions reduction from the additional
restrictions on non-fumigant pesticide;
however, the restrictions are part of
CDPR’s regulatory program to ensure
that the inventory target of 18.1 tpd in
the SJV is not exceeded (Id. at page 1),
which effectively defines the needed
stringency. This commitment is
sufficiently clear and adequate to ensure
that is enforceable as required by CAA
section 110(a)(1)(A).
C. Reasonably Available Control
Measures/Reasonably Available Control
Technology (RACM/RACT) Requirement
Under CAA Sections 172(c)(1) and
182(b)(1)
CAA section 172(c)(1) requires that
each attainment plan ‘‘provide for the
implementation of all reasonably
available control measures as
expeditiously as practicable (including
such reductions in emissions from
existing sources in the area as may be
obtained through the adoption, at a
minimum, of reasonably available
control technology), and shall provide
for attainment of the national primary
ambient air quality standards.’’ RACM is
a requirement only for nonattainment
areas.
EPA defines RACM as any potential
control measure for application to point,
area, on-road and non-road emissions
source categories that meets certain
criteria. These criteria include whether
the measure is technologically and
economically feasible and either
individually or collectively with other
RACM can advance the attainment date
by at least one year. See 57 FR 13498,
13560 (April 16, 1992). The
determination as to whether a SIP
provides for the implementation of
RACM as required by CAA section
172(c)(1) is done as part of an area’s
attainment and reasonable further
progress plans and not on a rule-by-rule
basis.
For ozone nonattainment areas
classified as moderate or above, CAA
section 182(b)(2) requires the
implementation of reasonably available
control technologies (RACT) on all
major sources of VOC 13 and for each
13 In areas classified as severe (such as SED,
Ventura, and Sacramento Metro), a major source is
a stationary source that emits or has the potential
to emit at least 25 tons of VOC or NOX per year.
See CAA sections 182(d) and (f). For extreme areas
(South Coast and SJV), a major stationary sources
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VOC source category for which EPA has
issued a Control Techniques Guideline
(CTG). CAA section 182(f) requires that
RACT under section 182(b)(2) also
apply to major stationary sources of
NOX. See CAA sections 182(d) and (f).
The proposed revisions to the
California SIP Pesticide Element that we
are evaluating here are intended to
reduce VOC emissions in the South
Coast, SED, Ventura, SJV, and
Sacramento Metro ozone nonattainment
areas. VOC emissions contribute to the
formation of ozone and secondary
particulate matter. EPA, though, has
determined by rule that states do not
need to address controls for sources of
VOC emissions for PM2.5 standard
attainment unless the state and/or EPA
make a technical demonstration that
such controls would significantly
contribute to reducing PM2.5
concentrations in the nonattainment
area. See 40 CFR 51.1002(c)(3). Such a
determination would be made in the
context of each area’s plan for
attainment of the PM2.5 standards. Of
the areas subject to the California SIP
Pesticide Element, only the South Coast,
SJV, and Sacramento Metro areas are
nonattainment for one or more of the
PM2.5 standards and only South Coast
controls VOC for PM2.5 attainment.
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Field Fumigant Regulations
CARB’s 2009 submittal of the field
fumigant regulations did not include a
demonstration of how the field
fumigation methods implement
RACT.14 In response to EPA comments,
CDPR provided a document containing
more detailed information on its RACT
evaluation of fumigation methods.15
This document contains a general
discussion of strategies for controlling
VOC emissions from fumigants and an
evaluation of field fumigation method
options, including the basis for those
accepted and those rejected by CDPR for
inclusion in its regulations. It discusses
current research on fumigant VOC
emission reduction methods, including
a reevaluation of fumigants to obtain
additional data to replace surrogate data
used in developing the adopted
regulations.
Field fumigation emissions are
considered fugitive emissions because
they are emissions that ‘‘could not
is one that emits or has the potential to emit at least
10 tons of VOC or NOX per year. See CAA sections
182(e) and (f).
14 See letter, Andrew Steckel, EPA Region 9 to
Frank Spurlock, CDPR and Mike Guzzetta, CARB,
November 2, 2010.
15 See letter and attachments, Randy Segawa,
CDPR to Andrew Steckel, EPA–Region 9, Reducing
Volatile Organic Compound Emissions from
Pesticides: Analysis of Alternatives for Field
Fumigation Methods, June 28, 2011.
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reasonably pass through a stack,
chimney, vent, or other functionallyequivalent opening.’’ 16 As noted above,
CAA section 182(b)(1) requires RACT be
applied to all to major stationary
sources in a ozone nonattainment area
classified moderate or above. EPA has
not yet defined by rule whether fugitive
emissions must be included in
determination of major source status for
the purposes determining the
application of section 182(b)(1) RACT
requirement; however, EPA believes,
based on the information provided in
the CDPR’s alternatives analysis, and
the research cited to support it, that
CDPR has demonstrated that the
proposed regulations are stringent
enough to implement RACT-level
controls on the application of
pesticides.
On January 10, 2012, EPA partially
approved and partially disapproved the
section 182(b)(1) RACT SIP submitted
by California on June 18, 2009 for the
SJV ozone nonattainment area. The
partial disapproval was based in part on
our conclusion that the State had not
fully satisfied CAA section 182(b) RACT
requirements for the application of
fumigants. See 77 FR 1417, 1425
(January 10, 2012). Based on our
proposed finding here that CDPR’s field
fumigant regulations provide RACTlevel controls on this source category,
final approval of these regulations
would satisfy California’s obligation to
implement RACT under CAA section
182(b)(1) for this source category for the
1-hour ozone and 1997 8-hour ozone
standards for the SJV RACT SIP.
EPA has recently approved the
attainment, RFP and RACM
demonstrations in the 8-hour ozone SIPs
for the South Coast and San Joaquin
Valley and the PM2.5 SIP for the South
Coast (which did include VOC
reductions in its RFP and attainment
demonstrations).17 These
demonstrations relied in part on VOC
control measures in the 2007 State
Strategy; however, EPA’s approval of
these demonstrations did not rely on
emissions reductions from CDPR’s field
fumigant regulations. Therefore, their
16 See
40 CFR 70.2 (Definitions).
76 FR 69928 (November 9, 2011) (South
Coast PM2.5 Plan), 77 FR 12652 (March 1, 2012) (SJV
2007 8-hour Ozone SIP), and 77 FR 12674 (March
1, 2012) (South Coast 8-hour Ozone Plan). EPA has
also recently approved the SJV 2008 PM2.5 SIP
which relied in part on measures in the 2007 State
Strategy. In approving that SIP, EPA concurred with
the State’s determination that VOC did not need to
be controlled for PM2.5 attainment in the SJV and
therefore the plan did not include did not need to
evaluate VOC control measures as part of its RACM
demonstration. See 76 FR 69896, 69924 (November
9, 2011). The PM2.5 plan for the Sacramento Metro
area is not due until late 2012.
17 See
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24445
approval into the SIP is consistent with
the approved RACM demonstrations.
CARB has submitted SIPs to address
attainment of the 1997 8-hour ozone
standard in the SED, Ventura County,
and Sacramento Metro nonattainment.
EPA has not yet acted on these plans
although we note that none rely on
reductions from controls on pesticides.
Pesticide Emission Reduction
Commitment for the San Joaquin Valley
As noted above, the demonstration
that a SIP provides for the
implementation of RACM as required by
CAA section 172(c)(1) is done as part of
an area’s attainment and reasonable
further progress plans and not on an
individual rule or commitment basis.
EPA recently approved the 2007
8-hour ozone SIP for the San Joaquin
Valley, including the SIP’s RACM
demonstration. 77 FR 12652 (March 1,
2012). To demonstrate that the SIP
provided for RACM, California relied in
part on measures in the 2007 State
Strategy, including the ‘‘Pesticide
Emission Reduction Commitment for
the San Joaquin Valley’’ (as revised
April 17, 2009) that we are proposing to
approve here. However, because we had
not yet approved the commitment into
the SIP, we did not grant any emissions
reductions credit to the commitment in
either the RFP or attainment
demonstration nor did we rely on it to
make our determination that the 2007
SIP provided for RACM. See Air
Division, EPA Region 9, ‘‘Final
Technical Support Document and
Response to Comments Final Rule on
the San Joaquin Valley 2007 Ozone Plan
and the San Joaquin Valley Portions of
the 2007 State Strategy,’’ December 15,
2011, pp. 51–57. Because EPA’s
approvals of the attainment, RFP, and
RACM demonstrations in the SJV 2007
8-hour ozone SIP did not rely on
emissions reductions from CDPR’s
commitment to limit pesticide VOC
emissions in the SJV to 18.1 tpd, its
approval into the SIP is consistent with
the approved RACM demonstration.
D. Finding of Non-Interference With
Applicable Requirements of the CAA
Under Section 110(l)
Revisions to the SIP, including
revisions to SIP-approved control
measure, must meet the requirements of
CAA section 110(l) to be approved by
EPA. CAA section 110(l) ‘‘Plan
Revisions’’ provides in relevant part:
The Administrator shall not approve a
revision of a plan if the revision would
interfere with any applicable requirement
concerning attainment and reasonable further
progress (as defined in [section 171]) or any
other applicable requirement of [the CAA].
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We interpret section 110(l) to apply to
all requirements of the CAA and to all
areas of the country, whether
attainment, nonattainment,
unclassifiable, or maintenance for one
or more of the six criteria pollutants. We
also interpret section 110(l) to require a
demonstration addressing all pollutants
whose emissions and/or ambient
concentrations may change as a result of
the SIP revision. The scope and rigor of
an adequate section 110(l)
demonstration of noninterference
depends on the air quality status of the
area, the potential impact of the revision
on air quality, the pollutant(s) affected,
and the nature of the applicable CAA
requirements.
In reviewing a modification to an
approved SIP provision, we look to see
to what extent the existing SIP has
relied on that provision to meet
applicable CAA requirements. For
emissions reduction measures, we
generally conclude that the revision will
not interfere with any applicable
requirement related to attainment or
RFP if the revised SIP will provide the
same or more emissions reductions on
the same or similar schedule as the
existing SIP. We note, however, that
CAA section 110(l) does not bar
approval of SIP revisions that may result
in higher levels of emissions than would
potentially occur under the unrevised
SIP; only that such revisions do not
result in the applicable SIP no longer
providing for expeditious attainment or
RFP or complying with any other
applicable requirements of the CAA.
The submittals that we are evaluating
in this proposal for inclusion into the
California SIP control VOC emissions in
five California areas. Neither the field
fumigant regulations nor the SJV
pesticide SIP commitment explicitly
regulated any other pollutant besides
VOC. VOC is a precursor pollutant for
ozone as well as for both fine (PM2.5)
and coarse (PM10) particulate matter.18
At this time, only the South Coast’s SIP
relies on VOC controls for PM2.5 or PM10
attainment and none of its adopted
particulate matter plans rely on
reductions from the California SIP
Pesticide Element (either as already
approved or proposed for approval here)
to demonstrate attainment, RFP, or
RACM or to meet any other requirement
of the CAA.
Field Fumigant Regulations
The CDPR’s field fumigant regulations
are the first such regulations
18 As noted previously, while EPA considers VOC
to be a precursor to PM, it does not require control
of VOC emissions for PM standard attainment in
most instances. See 72 FR 20586, 20589 (April 25,
2007) and 57 FR 13498, 13538 (April 16, 1992).
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incorporated into the California SIP.
Their approval will strengthen the SIP
by providing SIP-enforceable measures
and compliance procedures to reduce
emissions from the application of
fumigants in the five ozone
nonattainment areas covered by the
regulations. Their approval will also aid
compliance with the approved
California SIP Pesticide Element’s
provisions for reducing VOC emissions
by 20 percent from 1990 baseline levels
in the South Coast, SED, Ventura, and
Sacramento Metro ozone nonattainment
areas. Their approval will also aid
compliance with the proposed 18.1 tpd
limit on pesticide VOC emissions in the
San Joaquin Valley. Therefore, EPA
proposes to find that approving the field
fumigant regulations into the California
SIP will not interfere with any
applicable requirement concerning
attainment and reasonable further
progress or with any other applicable
requirement of the CAA.
Pesticide Emission Reduction
Commitment for the San Joaquin Valley
In 1997, EPA approved the 1994
Pesticide Element into the California
SIP. See 62 FR 1150, 1170 (January 8,
1997). As approved, the Element’s goal
was to reduce VOC emissions from
agricultural and commercial structural
pesticide applications by a maximum of
20 percent from the 1990 baseline
emission inventory by 2005 in areas that
relied on VOC reductions from
pesticides in their attainments plans
with reductions to occur linearly from
1990 to 2005 but it allowed for less than
20 percent if fewer VOC reductions from
pesticide were needed. See ‘‘The State
Implementation Plan for Agricultural
and Commercial Structural Pesticides,’’
November 15, 1994 (‘‘1994 Pesticide
SIP’’), p. 1.19
The attainment demonstration for the
SJV in the 1994 Ozone SIP relied in part
on reductions of 12 percent from 1990
emissions levels from the 1994 Pesticide
Element to demonstrate attainment by
the area’s then-applicable attainment
deadline of November 15, 1999. In
approving the 1994 Pesticide Element
and the SJV ozone attainment
demonstration, EPA credited the
19 As submitted, the 1994 Pesticide Element
consisted of three documents: the 1994 Pesticide
SIP and the memorandum from James W. Wells,
Director, CDPR, to James D. Boyd, Executive
Officer, CARB, May 9, 1995 (‘‘Wells
memorandum’’) and the letter from James D. Boyd,
Executive Officer, CARB, to David Howekamp,
Division Director, EPA–Region 9, June 13, 1996
(‘‘Boyd Letter’’). As approved, it consisted of the
1994 Pesticide SIP (40 CFR 52.220(c)(204)(i)(A)(6))
and the Boyd letter (40 CFR 52.220(c)(236)). See
section IV of this preamble for further discussion
of the 1994 Pesticide Element.
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element with 13 tpd (in 1994 SIP
currency 20) in VOC emissions
reductions in 1999.21 At the same time,
EPA noted that California had
committed to adopt and submit any
regulations necessary to reduce VOC
emissions from agricultural and
commercial structural pesticides by 12
percent in 1999 22 in SJV. See 61 FR
10920, 10935 (March 18, 1996).
In 2003, CARB updated the strategy
that was part of the 1994 Ozone SIP.
One of the measures in the 2003 State
Strategy was PEST–1 (‘‘Implement
Existing Pesticide Strategy’’), which
retained the provisions of the 1994
Pesticide Element. In 2004, CARB
submitted the 2004 Extreme [1-hour
Ozone] Attainment Plan for the SJV 23
which relied in part on the 2003 State
Strategy for the reductions needed to
demonstrate attainment by SJV’s new
applicable attainment date of November
15, 2010. On page 27 of its staff report
for that plan,24 CARB discusses the
measures in the 2003 State Strategy
including PEST–1. It describes the
measure as a ‘‘[c]ontinuation of the
Department of Pesticide Regulation’s
approved SIP obligation to reduce
volatile emissions from pesticides
[which f]or the San Joaquin Valley
* * * means a pesticide VOC emissions
20 A SIP’s ‘‘currency’’ is the emissions inventory
on which it is based. An emissions reduction
expressed in a particular ‘‘SIP currency’’ is an
emissions reduction calculated using the inventory
included in that SIP. Because inventories vary from
SIP to SIP for reasons unrelated to controls (e.g.,
improved activity estimates or emissions factors),
the estimated emissions reductions from a control
measure in tons per day can change from SIP to SIP
even if the effectiveness of the control measure as
a percentage of the emissions category does not.
21 The 13 tpd figure was provided by CARB on
page A–2 and in Attachment C of the Boyd Letter.
For the 1994 Ozone SIP, the State estimated that
VOC emissions from pesticide use in 1990 in the
San Joaquin Valley were 62.5 tpd. A 12 percent
reduction from this level would require reducing
overall pesticide emissions to be no more than 55.0
tpd in 1999. The State further estimated that
without controls, VOC emissions from pesticides in
the SJV would increase to 67.9 tpd by 1999, thereby
requiring a reduction of 12.9 tpd (67.9 tpd minus
55.0 tpd, rounded to 13 tpd) in 1999 in order to
meet the target level for a 12 percent reduction. See
CDPR, Staff Report on the Department of Pesticide
Regulation’s Proposed SIP Commitment for San
Joaquin Valley,’’ undated, p. 1, ftn 1.
22 A 20 percent reduction that was to occur
linearly over the fifteen years between 1990 and
2005 would accrue reductions at a rate of 1.33
percent per year (20 percent divided by 15 years)
resulting in a 12 percent reduction by 1999 (9 years
times 1.33 percent per year).
23 San Joaquin Valley Air Pollution Control
District, ‘‘Extreme Ozone Attainment
Demonstration Plan’’ adopted October 8, 2004;
amended October 20, 2005 and August 21, 2008.
24 CARB, Staff Report, Proposed 2004 State
Implementation Plan For Ozone In The San Joaquin
Valley, Release Date: September 28, 2004.
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target of 12 percent less than 1990
levels.’’
EPA approved PEST–1 into the SIP as
part of its action to approve in part and
disapprove in part the 2003 South Coast
AQMP. See 74 FR 10176 (March 10,
2009), codified at 40 CFR
52.220(c)(ii)(A)(1). We have not
approved any other changes to the SJVrelated provisions of 1994 Pesticide
Element nor have we granted any
emissions reductions credit for the 1994
Pesticide Element beyond the 13 tpd (in
1994 SIP currency) approved as part of
our action on the 1994 Ozone SIP.25
California is now proposing to revise
its SIP Pesticide Element for the SJV to
replace the requirement to achieve a
percent reduction in VOC emissions
from pesticides with a limit on overall
VOC emissions from pesticides in the
SJV of 18.1 tpd of VOC during the high
ozone season of May 1 to October 31.
The 18.1 tpd cap equates to a reduction
of 12 percent from the current estimate
of 1990 pesticide VOC emissions levels
in the SJV.26
Based on our review of the proposed
revision, we find that the revision will
result in, at minimum, the same
emissions reductions that are currently
required by the approved SIP and will
not delay those reductions given that
the limit is currently effective. We,
therefore, propose to find that approving
CDPR’s commitment to manage VOC
emissions from agricultural and
commercial structural pesticide use to
ensure that they do not exceed 18.1 tpd
in the SJV area into the California SIP
will not interfere with any requirement
concerning attainment and reasonable
further progress or any other applicable
requirement of the CAA.
In comments that EPA received on its
proposed approval of the SJV 2004
Extreme Ozone Attainment Plan (74 FR
33933(July 14, 2009)), several nongovernmental organizations argued that
the 1994 Pesticide Element requires a 20
percent reduction in VOC emissions
from 1990 levels by 2005 in the SJV
citing to the Boyd letter on page A–2.27
25 We have approved two ozone plans for the SJV
since the 1997: the 2004 Ozone Plan in 2010 and
the second, the 2007 8-hour Ozone Plan in 2012.
See 75 FR 10420 (March 8, 2010) and 77 FR 12652
(March 1, 2012). Neither plan nor our approval of
them relied on reductions in pesticide emissions to
meet any applicable CAA requirement.
26 See CDPR, Staff Report on the Department of
Pesticide Regulation’s Proposed SIP Commitment
for San Joaquin Valley,’’ undated (enclosure 2 to
memorandum, Christopher W. Reardon, Chief
Deputy Director, CDPR, to James Goldstene,
Executive Officer, CARB, October 5, 2009; subject:
Amendments to the Pesticide Element of the Ozone
State Implementation Plan).
27 See letter, Brent Newell, Legal Director, Center
on Race, Poverty & the Environment, August 31,
2009, ‘‘Comments on Approval and Promulgation of
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In the Boyd letter, CARB provided
EPA with suggested revisions to our
March 18, 1996 (61 FR 10920, 10935)
proposed approval of the 1994 Ozone
SIP. In reference to the 1994 Pesticide
Element, CARB stated that the
‘‘commitment is for a 20% reduction
from 1990 levels by 2005 in each SIP
area, except [San Diego]. [CARB] only
took credit in the attainment year: SJV
1999 = 12%; Sac 2005 = 20%; Ven 2005
= 20%; SED 2007 = 20%; SC 2010 =
20%.’’ EPA does not find the
‘‘commitment is for a 20% reduction’’
statement determinative as to the State’s
commitment for SJV, not only because
it is immediately contradicted by the
statement that a 12 percent credit was
taken only in the attainment year of
1999 but also because it is not entirely
consistent with the more extensive
language describing the emissions
reductions target in other parts of the
approved 1994 Pesticide Element and
does not reflect the reductions relied on
in the SIP.
The 1994 Pesticide Element
committed CDPR to a ‘‘maximum of 20
percent’’ reduction in pesticide VOC
emissions from 1990 baseline levels in
areas ‘‘which reference VOC
reductions’’ from the element in their
plans. See 1994 Pesticide SIP, p. 1. With
this language, the percent reduction
required in an area is tied to the
emissions reductions referenced, that is,
relied on, in that area’s plan. As
approved, the 1994 Pesticide Element
also allowed for reductions of less than
20 percent if fewer VOC reductions from
pesticide were needed. Id. As noted
above, the reductions relied on in the
1994 Ozone SIP in its attainment
demonstration for SJV in 1999 were 13
tpd (in 1994 SIP currency) which
equates to 12 percent reduction from
1990 baseline in 1999 (when anticipated
growth in pesticide VOC emissions
between 1990 and 1999 is excluded)
and no additional reductions have been
relied on in any SIP for SJV subsequent
to the 1994 one.
Approval of the revised ‘‘Pesticide
Emission Reduction Commitment for
the San Joaquin Valley’’ (submitted in
2009) will not interfere with any
applicable requirement related to
attainment or reasonable further
progress for any PM2.5 or PM10 standard
in the SJV. EPA has determined that
VOC controls are not required for
particulate matter control in the SJV.
See 72 FR 20586, 20589 (April 25,
2007), 69 FR 30006, 30007 (May 26,
Implementation Plans: 1-Hour Ozone Extreme Area
Plan for San Joaquin Valley, CA (Docket No. EPA–
R09–OAR–2008–0693),’’ pp. 16–20.
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2004), and 76 FR 69896, 69924
(November 9, 2011).
Additional information on EPA’s
determination under CAA section 110(l)
can be found in section II.D. of the TSD
for this proposal.
IV. Response To Remand in Association
of Irritated Residents Case
In this section, we discuss why EPA
believes that our proposed approval of
the fumigant regulations and
commitment for the SJV obviate the
need to rescind or modify EPA’s
previous approvals of the California SIP
Pesticide Element notwithstanding the
deficiencies in the 1994 Pesticide
Element that have been brought to light
by subsequent litigation. In so doing, we
summarize the relevant background that
provides the context for this
explanation.
In 1994, California submitted the 1994
Pesticide SIP as part of its
comprehensive 1994 Ozone SIP. The
1994 Pesticide SIP set forth the goal of
reducing VOC emissions from pesticide
use by as much as 20 percent from 1990
levels as needed in those areas of
California that relied on emissions
reductions from pesticides to meet CAA
requirements for attainment of the
1-hour ozone standard. The 1994
Pesticide SIP included a process for reevaluation of pesticide products (to
refine emissions estimates and to review
for possible restrictions on use), for
establishing the 1990 base year
inventory and for tracking emissions, for
reducing VOC emissions from pesticide
use through voluntary changes in pest
management practices, and for
developing additional regulatory
measures to ensure that reductions are
achieved.
Upon review of the 1994 Pesticide
SIP, EPA identified certain
completeness and approvability issues
and requested clarification. See letters,
David P. Howekamp, Director, Air and
Toxics Division, EPA Region 9 to James
W. Wells, Director, CDPR, March 20,
1995 and April 21, 1995. CDPR
responded to EPA’s request with a
clarification of the 1994 Pesticide SIP
that established a commitment on the
part of CDPR ‘‘to adopt and submit to
U.S. EPA by June 15, 1997, any
regulations necessary to reduce [VOC]
emissions from agricultural and
commercial structural pesticides by
specific percentages of the 1990 base
year emissions, by specific years, and in
specific nonattainment areas,’’ as listed
in a table showing percent reductions of
8, 12, 16, and 20 percent by 1996, 1999,
2002, and 2005, respectively, in the
following nonattainment areas: South
Coast, Southeast Desert, Ventura, San
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Joaquin Valley, and Sacramento Metro.
See letter, James W. Wells, Director,
CDPR, to David P. Howekamp, EPA
Region 9, March 31, 1995; the Wells
memorandum; and the related
transmittal letter for the Wells
memorandum from James D. Boyd,
Executive Officer, CARB to Felicia
Marcus, Regional Administrator, EPA
Region 9, May 11, 1995.
In March 1996, EPA proposed to
approve the 1994 Pesticide Element,
among other elements of the 1994
Ozone SIP and did so based in part on
the clarification provided by CDPR
through the Wells memorandum. See 61
FR 10920, 10935–10936 (March 18,
1996). In response to EPA’s proposed
rule, CARB submitted a letter stating:
‘‘In the pesticide element of the SIP, the
[CDPR] projected a steady decline in
volatile emissions from pesticides
between 1996 and 2005. However,
California took SIP credit for these
reductions only in the applicable
attainment year for the San Joaquin
Valley, Sacramento Region, Ventura
County, the Southeast Desert, and the
South Coast. The notice should reflect
this information.’’ See letter, James M.
Strock, Secretary for Environmental
Protection, California Environmental
Protection Agency, to Felicia Marcus,
Regional Administrator, EPA Region 9,
May 2, 1996. CARB subsequently
submitted the Boyd Letter providing
additional detail that was intended to
supplement the technical corrections
identified in the State’s formal May 2
comment letter. Through the Boyd
Letter, CARB clarified again that CDPR’s
commitment was for a 20 percent
reduction from 1990 levels by 2005 in
the five specified nonattainment area
but also noted that CARB only took
credit in the attainment year, which
CARB specified as a 12 percent
reduction by 1999 in San Joaquin
Valley, and 20 percent reduction in the
attainment years for the four other
nonattainment areas.28
In 1997, EPA took final action to
approve the 1994 Pesticide Element,
and most of the 1994 California Ozone
SIP and again referred to the Wells
memorandum as providing the
clarification necessary to provide EPA
28 At the time of EPA’s action on the 1994
California Ozone SIP and related 1994 Pesticide
Element, the SJV was classified as a ‘‘serious’’
nonattainment area for the 1-hour ozone standard
with an applicable attainment date of 1999. See 61
FR 10920, 10925. Years after approval of the 1994
SIP, the SJV was reclassified as ‘‘severe’’ and then
‘‘extreme’’ for the 1-hour ozone standard. See 66 FR
56476 (November 8, 2001) and 69 FR 20550 (April
16, 2004).The other four areas were classified as
‘‘severe’’ or ‘‘extreme’’ with later attainment dates
at the time of EPA’s action on the ozone SIP and
Pesticide Element.
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with the basis to approve the 1994
Pesticide Element as meeting the
applicable requirements for
enforceability of SIP revisions. See 62
FR 1150, 1169–1170 (January 8, 1997).
However, in the 1997 final rule, EPA
referred explicitly to California’s request
in its May 2, 1996 comment letter to
exclude emissions reductions for
interim years from the SIP, and also
implicitly referred to the Boyd Letter by
citing CARB’s decision not to assign
credit to the pesticides measure except
for purposes of attainment. In the final
rule, we tried to reconcile the Wells
memorandum with California’s
comment letter and the Boyd letter and
summarized what we believed the
Pesticide Element to contain with
respect to regulatory measures, as
follows: ‘‘As described in the SIP,
California has committed to adopt and
submit to U.S. EPA by June 15, 1997,
any regulations necessary to reduce
VOC emissions from agricultural and
commercial structural pesticides by 20
percent of the 1990 base year emissions
in the attainment years for Sacramento,
Ventura, Southeast Desert, and the
South Coast, and by 12 percent in 1999
for the San Joaquin Valley.’’ Id. at 1170.
In listing the specific portions of the
1994 Ozone SIP and related documents
that we were approving and
incorporating as part of the California
SIP in our 1997 final action, we listed
CDPR’s 1994 Pesticide SIP and the Boyd
Letter, but did not list the Wells
memorandum. While EPA’s failure to
approve and incorporate the Wells
memorandum into the SIP may have
been inadvertent, California’s May 2,
1996 comment letter and the Boyd
Letter made such approval and
incorporation (i.e., without
modification) problematic because the
Wells memorandum contained interim
year emissions reduction commitments
that the California comment letter and
Boyd Letter specifically excluded.
In the mid-2000’s, several community
groups sued CDPR under the CAA for
failure to adopt and submit regulations
ensuring VOC emissions reductions
from pesticide use in Ventura County
based on the commitments set forth in
the Wells memorandum. Upon review
of the record, the Ninth Circuit Court of
Appeals in effect denied the community
group the remedy that the group sought
based on the court’s determination that
the Wells memorandum was not in fact
approved into the California SIP and
thus the commitment by CDPR to adopt
and submit regulations as set forth in
the Wells memorandum was not
enforceable under the Act. See El
´
Comite para el Bienestar de Earlimart v.
Warmerdam, 539 F.3d 1062 (9th Cir.
PO 00000
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Fmt 4702
Sfmt 4702
2008) (Warmerdam). In the wake of the
Warmerdam decision, the community
group filed a petition for review in the
Ninth Circuit challenging EPA’s 1997
approval of the 1994 Ozone SIP on the
grounds that, without the Wells
memorandum, EPA’s approval of that
SIP was arbitrary and capricious
because it relied on unenforceable
emissions reductions from the 1994
´
Pesticide Element. See El Comite para el
Bienestar de Earlimart v. EPA, No. 08–
´
74340 (‘‘El Comite’’). The Ninth Circuit
has not issued its decision in the El
´
Comite case against EPA’s approval of
the 1994 Ozone SIP.
Meanwhile, in 2004, California
resubmitted the 1994 Pesticide Element
to EPA as part of the 2003 State
Strategy, which was originally intended
to replace the state measures potion of
the 1994 California Ozone SIP in the
California SIP, in the form of a control
measure referred to as ‘‘PEST–1.’’
PEST–1 was simply a continuation of
the original 1994 Pesticide Element. In
2009, we approved PEST–1 as part of
our approval of the 2003 State Strategy
reasoning that approval or disapproval
of PEST–1 amounted to the same thing
from the standpoint of the California
SIP, namely the 1994 Pesticide Element.
See 74 FR 10176 (March 10, 2009).
EPA’s approval of PEST–1 was
challenged and the Ninth Circuit
disagreed with EPA’s decision that
approval or disapproval of PEST–1
amounted to the same thing and
remanded the approval of PEST–1 back
to EPA for an evaluation of the Pesticide
Element for enforceability. See
Association of Irritated Residents v.
EPA, 632 F.3d 584 (9th Cir. 2011),
revised January 27, 2012 (AIR).
Specifically, the Ninth Circuit held,
given its earlier finding in the
Warmerdam case that the Wells
memorandum was not approved and
incorporated into the California SIP,
that EPA must determine whether the
approved 1994 Pesticide Element has
sufficient enforcement mechanisms to
satisfy the requirements of the CAA. In
light of the decision in AIR, EPA filed
a supplemental brief that argues that the
decision in the AIR case makes the El
´
Comite case moot on the grounds that
the relief granted in the AIR case with
respect to PEST–1 amounts to the same
relief that the petitioner could gain by
´
a favorable decision in the El Comite
case, namely re-evaluation of the
Pesticide Element for enforceability.
´
The petitioners in the El Comite
disagree that the AIR decision has made
´
the El Comite case moot, and the Ninth
Circuit has not yet issued its decision in
´
the El Comite case.
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In light of the remand in the AIR case
and with due consideration to the
history summarized above, we must reevaluate the enforceability of the 1994
Pesticide Element recognizing that the
Wells memorandum is not approved
into the SIP and take appropriate
remedial actions if the element (without
the Wells memorandum) does not meet
the minimum requirements for
enforceability under the CAA. We are
using this proposed rule on the
submitted fumigant regulations and
revised SIP commitment for the SJV as
the opportunity to present our reevaluation and to explain our rationale
for taking no action to rescind or modify
our approvals of the 1994 Pesticide
Element in 1997 and again (as PEST–1)
in 2009.
First, we recognize that the 1994
Pesticide Element is a ‘‘committal’’
measure rather than a ‘‘control’’
measure. That is, the 1994 Pesticide
Element constitutes a measure for which
the State does not provide regulations
(or equivalent enforceable mechanism)
in support of the emissions reductions
credited to the measure at the time EPA
takes action on the RFP or attainment
demonstration plan that relies on the
emissions reduction, but commits to
adopt and submit regulations in support
of the emissions reductions prior to the
time when the reductions are needed for
RFP or attainment. EPA has found,
under certain circumstances, that
committal measures that are relied on to
meet RFP, attainment, and/or other
emissions reductions requirements of
the CAA to be enforceable, and thus
approvable, only if such measures
identify the responsible party,
applicability, adoption dates for rules (if
applicable), implementation dates, and
emissions reductions in terms of
emissions rates (such as tons per day)
equal to the credit taken in the RFP or
attainment plan for the committal
measure.
Back in 1995, when EPA reviewed the
1994 Pesticide SIP, we sought
clarification from CDPR on whether the
1994 Pesticide SIP establishes a
commitment to limit VOC emissions
from pesticides to specific percentages
of the 1990 base year emissions by
specific years in specific nonattainment
areas, regardless of future growth in
emissions that might otherwise occur
and whether the Pesticide Element
establishes a commitment to adopt any
regulations by a specific month prior to
the implementation date. See letter,
David P. Howekamp, Director, Air and
Toxics Division, EPA Region 9 to James
W. Wells, Director, CDPR, March 20,
1995. Later, we requested that CDPR
modify the SIP to be explicit as to the
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dates of rule adoption and submittal and
the emissions reductions by date and
area. See letter, David P. Howekamp,
Director, Air and Toxics Division, EPA
Region 9 to James W. Wells, Director,
CDPR, April 21, 1995. The clear
implication in EPA’s request to CDPR is
that EPA believed at the time that such
a modification of the 1994 Pesticide SIP
was necessary to meet the minimum
level of enforceability for crediting the
emissions reductions from such a
committal measure. CDPR’s response,
via CARB, was the Wells memorandum.
EPA’s views on acceptable committal
measures have not changed significantly
since the time of EPA’s review and
approval of the 1994 Pesticide Element
in 1997, and thus, we can infer from the
correspondence between EPA and CDPR
cited above and EPA’s statements in
both the 1996 proposed rule and 1997
final rule that, in the absence of the
Wells memorandum, EPA would not
have approved the 1994 Pesticide
Element on the grounds that it does not
meet the minimum level of
enforceability that the CAA requires.
See, generally, CAA section 110(a)(2)
(‘‘Each such plan shall (A) include
enforceable emission limitations and
other control measures, means, or
techniques * * * as may be necessary
or appropriate to meet the applicable
requirements of [the CAA]’’). We have
no reason to conclude otherwise today,
and thus, we affirm that, absent a
commitment providing the specificity
found in the Wells memorandum, the
1994 Pesticide Element does not meet
the minimum requirements for
enforceability of SIP committal
measures.
Second, we discuss what actions EPA
should take to address the deficiency in
enforceability of the 1994 Pesticide
Element as discussed above. We do so
recognizing that CDPR has, since EPA’s
approval of the 1994 Pesticide Element,
adopted and (via CARB) submitted
regulations that in effect have converted
many of the non-regulatory provisions
in the 1994 Pesticide Element into a
regulatory form. Specifically, CDPR has
adopted and submitted regulations
restricting the use of field fumigant
application methods; requiring CDPR to
annually inventory and report pesticide
VOC emissions for each area;
establishing pesticide use recordkeeping
and reporting requirements; and
creating a contingency field fumigation
limit and allowance program for
Ventura. These are the types of
regulations that the commitment in the
Well memorandum would have made
enforceable had the Wells memorandum
been approved into the SIP, and thus,
we find no need to perfect the
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24449
commitment to regulations in the 1994
Pesticide Element because the actual
submittal of the regulations themselves
obviates the need for an enforceable
commitment to submit those same
regulations.
While we believe that the submitted
CDPR regulations fulfill the otherwise
unenforceable commitment in the 1994
Pesticide Element to adopt and submit
regulations, the question remains
whether the regulations alone suffice to
ensure that the emission reduction
targets (20 percent from 1990 levels in
the South Coast, Southeast Desert,
Ventura, and Sacramento Metro areas
and 12 percent from 1990 levels in San
Joaquin Valley) are met. Based on our
review of the regulations for this
proposed action, we find that
compliance with the emission
reductions targets is provided through
CDPR regulations limiting field
fumigant application to lower-emitting
methods and establishing a fumigant
emissions limit and allocation system
for Ventura County and monitored and
enforced through regulations that
require recordkeeping and reporting of
pesticide usage and CDPR to annually
evaluate and report VOC emissions from
pesticides in each area.
These provisions are adequate to
ensure that the emission reduction
targets are met in the Sacramento Metro,
South Coast, and Southeast Desert areas
given that VOC emissions from
pesticide use are typically 60 percent
lower than 1990 levels in Sacramento
Metro and Southeast Desert and 80
percent lower than 1990 levels in the
South Coast. See CDPR’s Annual Report
on Volatile Organic Compound
Emissions from Pesticides: Emissions for
1990–2010 (March 2012), page 3. To a
large degree, the reductions in VOC
emissions from pesticide use (relative to
1990 levels) in these three areas have
resulted from permanent changes in
land use, although CDPR’s regulations
still serve an important function by
reducing the VOC emissions from
remaining pesticide use in the areas and
by establishing a regulatory mechanism
to track VOC emissions from this source
category that could, if necessary,
provide the basis for additional
regulatory measures if, for some reason,
VOC emissions from pesticide use were
to increase significantly over current
levels.
For Ventura County, in recognition
that VOC emissions from pesticide use
are predominantly from fumigant use
and are high enough that they could, in
a given year due to fluctuations in
pesticide use, violate the 20 percent
emission reduction target, CDPR has
submitted, and we are proposing to
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Federal Register / Vol. 77, No. 79 / Tuesday, April 24, 2012 / Proposed Rules
approve, additional regulatory
provisions for that area. These Venturaspecific provisions require CDPR to set
a field fumigant VOC emissions limit in
its annual VOC emissions inventory
report if overall pesticide emissions (not
just fumigant emissions) in the Ventura
nonattainment area are found to be
within five percent of or exceed the
listed benchmark. The benchmark is
equivalent to the 20 percent emissions
reduction target called for in the 1994
Pesticide Element for the Ventura area.
The Ventura-specific provisions also
require the county agricultural
commissioner to add conditions to field
fumigation permits or take other actions
to prevent the field fumigation limit
from being exceeded. As such, the
regulations reasonably ensure that the
20 percent emissions reduction target
would be met in Ventura County.
For the San Joaquin Valley, CDPR’s
regulations restricting fumigant
application methods and establishing
requirements on CDPR to inventory and
report VOC emissions from pesticide
use apply just as they do in the other
four nonattainment areas. While these
regulations and other measures have
decreased VOC emissions from
pesticide use in the SJV such that
current VOC emissions are
approximately 18 percent less than 1990
levels, CDPR concluded that a
mechanism was needed to supplement
the regulations to ensure that the 12
percent emission reduction target would
be met in the SJV. The supplemental
mechanism chosen by CDPR is the
adoption of a commitment, which we
are proposing to approve in today’s
action, to manage VOC emissions from
commercial structural and agricultural
pesticide use, such that the related VOC
emissions do not exceed 18.1 tons per
day in the SJV. This level of emissions
reflects a 12 percent emissions
reduction from 1990 level of VOC
emissions from pesticide use. The
specific measures that CDPR would
undertake to bring emissions back down
to that level in the event that the annual
inventory reveals that the 18.1 tons per
day emissions level had been exceeded
are not specified.29 Considered in
isolation, the revised commitment for
San Joaquin Valley changes the form of
the commitment in the 1994 Pesticide
Element for the SJV but does not
29 CDPR has presented options for these
measures. See CDPR presentation ‘‘Volatile Organic
Compound Emissions from Pesticides: Options for
Reducing Non-Fumigant Emissions’’ September
2011 and November 2011, which can be found at
https://www.cdpr.ca.gov/docs/emon/vocs/vocproj/
nonfum_options_091611.pdf https://
www.cdpr.ca.gov/docs/emon/vocs/vocproj/
nonfum_options_prec_111811.pdf.
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represent an enforceable measure for
SIP purposes. However, when viewed in
light of the CDPR’s regulations, the
combination of the commitment and
fumigant regulations does meet the
minimum requirements for
enforceability of SIP measures and
reasonably ensures that the 12 percent
emissions reduction target from the
1994 Pesticide Element would be
achieved in San Joaquin Valley.
For the reasons stated above, we
conclude that there is no need to
rescind or otherwise modify our 1997
approval of the 1994 Pesticide Element
or our 2009 approval of PEST–1
notwithstanding the deficiencies in
enforceability in the 1994 Pesticide
Element due to the absence of an
enforceable mechanism like the Wells
memorandum. In short, this is because
CDPR’s regulations and revised
commitment for the San Joaquin Valley
provide the enforceable mechanism that
would otherwise be lacking in the 1994
Pesticide Element. If EPA approves the
regulations and commitment, as
proposed herein, then the 1994
Pesticide Element would be fulfilled. If,
after consideration of comments, EPA
concludes that the regulations and
commitment do not meet the applicable
CAA requirements, then the decision
regarding EPA’s previous actions on the
1994 Pesticide Element would need to
be reconsidered.
V. Proposed Actions and Opportunity
for Public Comment
For the reasons discussed above, EPA
is proposing to approve under CAA
section 110(k)(3) the revisions to the
California SIP Pesticide Element
submitted by CARB on October 12, 2009
and August 2, 2011 and to incorporate
them into the California’s federallyenforceable SIP. We are deferring action
on the set of regulations submitted by
CARB August 2, 2011 related to
incorporating requirements related to
methyl iodide into the fumigant
regulations.
Based on the proposed approval of
these SIP revisions, EPA does not plan
to rescind or modify the Agency’s prior
approvals of the Pesticide Element
because the Agency has concluded that
the revisions fulfill the commitments of
the original Pesticide Element, thus
obviating the need to address the
deficiencies in enforceability of those
original commitments.
We encourage the public to comment
on these proposals. Comments will be
accepted for 30 days following
publication of the proposal in the
Federal Register. The deadline and a
list of options for submitting comments
is provided at the DATES and ADDRESSES
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Fmt 4702
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sections at the beginning of this
preamble.
VI. Statutory and Executive Order
Reviews
Under the CAA, 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,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely proposes to approve state law as
meeting Federal requirements and does
not propose to 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 Order 12866 (58 FR 51735
(October 4, 1993));
• 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 CAA; and
• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629 (February 16, 1994)).
In addition, this proposed action does
not have Tribal implications as
specified by Executive Order 13175 (65
FR 67249; November 9, 2000), because
the SIP is not approved to apply in
Indian country located in the State, and
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Federal Register / Vol. 77, No. 79 / Tuesday, April 24, 2012 / Proposed Rules
40 CFR Part 62
Protection Agency, 77 West Jackson
Boulevard, Chicago, Illinois 60604.
• Hand Delivery: Carlton T. Nash,
Chief, Toxics and Global Atmosphere
Section, Air Toxics and Assessment
Branch (AT–18J), U.S. Environmental
Protection Agency, 77 West Jackson
Boulevard, Chicago, Illinois 60604.
Such deliveries are only accepted
during the Regional Office normal hours
of operation, and special arrangements
should be made for deliveries of boxed
information. The Regional Office official
hours of business are Monday through
Friday, 8:30 a.m. to 4:30 p.m. excluding
Federal holidays.
Please see the direct final rule which
is located in the Rules section of this
Federal Register for detailed
instructions on how to submit
comments.
[EPA–R05–OAR–2012–0087; FRL–9663–5]
FOR FURTHER INFORMATION CONTACT:
Direct Final Approval of Hospital/
Medical/Infectious Waste Incinerators
State Plan for Designated Facilities
and Pollutants: Illinois
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
Margaret Sieffert, Environmental
Engineer, Environmental Protection
Agency, Region 5, 77 West Jackson
Boulevard (AT–18J), Chicago, Illinois
60604, (312) 353–1151,
sieffert.margaret@epa.gov.
SUPPLEMENTARY INFORMATION:
EPA notes that it will not impose
substantial direct costs on Tribal
governments or preempt Tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Ozone, Reporting and
recordkeeping requirements, Volatile
organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: April 13, 2012.
Jared Blumenfeld,
Regional Administrator, Region 9.
[FR Doc. 2012–9850 Filed 4–23–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
AGENCY:
EPA is proposing to approve,
through direct final rulemaking, Illinois’
revised State Plan to control air
pollutants from Hazardous/Medical/
Infectious Waste Incinerators (HMIWI).
The Illinois Environmental Protection
Agency submitted the revised State Plan
on November 8, 2011 and supplemented
it on December 28, 2011, following the
required public process. The revised
State Plan is consistent with Emission
Guidelines promulgated by EPA on
October 6, 2009. This approval means
that EPA finds that the revised State
Plan meets applicable Clean Air Act
requirements for subject HMIWI units.
Once effective, this approval also makes
the revised State Plan Federally
enforceable.
SUMMARY:
Comments must be received on
or before May 24, 2012.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2012–0087, by one of the
following methods:
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• Email: nash.carlton @epa.gov.
• Fax: (312) 886–6030.
• Mail: Carlton T. Nash, Chief, Toxics
and Global Atmosphere Section, Air
Toxics and Assessment Branch
(AT–18J), U.S. Environmental
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In the
Rules section of this Federal Register,
EPA is approving the State’s submittal
as a direct final rule without prior
proposal because the Agency views this
as a noncontroversial submittal and
anticipates no adverse comments. A
detailed rationale for the approval is set
forth in the direct final rule. If no
adverse comments are received in
response to this rule, no further activity
is contemplated. If EPA receives adverse
comments, the direct final rule will be
withdrawn and all public comments
received will be addressed in a
subsequent final rule based on this
proposed rule. EPA will not institute a
second comment period. Any parties
interested in commenting on this action
should do so at this time. Please note
that if EPA receives adverse comment
on an amendment, paragraph, or section
of this rule and if that provision may be
severed from the remainder of the rule,
EPA may adopt as final those provisions
of the rule that are not the subject of an
adverse comment. For additional
information, see the direct final rule
which is located in the Rules section of
this Federal Register.
Dated: April 9, 2012.
Susan Hedman,
Regional Administrator, Region 5.
[FR Doc. 2012–9711 Filed 4–23–12; 8:45 am]
BILLING CODE 6560–50–P
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24451
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 62
[EPA–R05–OAR–2012–0086; FRL–9663–3]
Direct Final Approval of Hospital/
Medical/Infectious Waste Incinerators
State Plan for Designated Facilities
and Pollutants: Indiana
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
EPA is proposing to approve,
through direct final rulemaking,
Indiana’s revised State Plan to control
air pollutants from Hazardous/Medical/
Infectious Waste Incinerators (HMIWI).
The Indiana Department of
Environmental Management submitted
the revised State Plan on December 19,
2011, following the required public
process. The revised State Plan is
consistent with Emission Guidelines
promulgated by EPA on October 6,
2009. This approval means that EPA
finds that the revised State Plan meets
applicable Clean Air Act requirements
for subject HMIWI units. Once effective,
this approval also makes the revised
State Plan Federally enforceable.
DATES: Comments must be received on
or before May 24, 2012.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2012–0086, by one of the
following methods:
1. www.regulations.gov: Follow the
on-line instructions for submitting
comments.
2. Email: nash.carlton@epa.gov.
3. Fax: (312) 886–6030.
4. Mail: Carlton T. Nash, Chief, Toxics
and Global Atmosphere Section, Air
Toxics and Assessment Branch (AT–
18J), U.S. Environmental Protection
Agency, 77 West Jackson Boulevard,
Chicago, Illinois 60604.
5. Hand Delivery: Carlton T. Nash,
Chief, Toxics and Global Atmosphere
Section, Air Toxics and Assessment
Branch (AT–18J), U.S. Environmental
Protection Agency, 77 West Jackson
Boulevard, Chicago, Illinois 60604.
Such deliveries are only accepted
during the Regional Office normal hours
of operation, and special arrangements
should be made for deliveries of boxed
information. The Regional Office official
hours of business are Monday through
Friday, 8:30 a.m. to 4:30 p.m. excluding
Federal holidays.
Please see the direct final rule which
is located in the Rules section of this
Federal Register for detailed
instructions on how to submit
comments.
SUMMARY:
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Agencies
[Federal Register Volume 77, Number 79 (Tuesday, April 24, 2012)]
[Proposed Rules]
[Pages 24441-24451]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-9850]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R09-OAR-2012-0194; FRL-9664-5]
Approval and Promulgation of Implementation Plans; California;
Revisions to the California State Implementation Plan Pesticide Element
AGENCY: U.S. Environmental Protection Agency (EPA).
ACTION: Proposed rule.
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SUMMARY: EPA proposes to approve several revisions to the Pesticide
Element of the California state implementation plan (SIP). These
revisions include regulations adopted by the California Department of
Pesticide Regulation (CDPR) that: (1) Reduce volatile organic compound
(VOC) emissions from the application of agricultural field fumigants in
the South Coast, Southeast Desert, Ventura, San Joaquin Valley (SJV),
and Sacramento Metro ozone nonattainment areas by restricting fumigant
application methods; (2) establish a contingency fumigant emissions
limit and allocation system for Ventura; (3) require CDPR to prepare
and make available to the public an annual pesticide VOC emissions
inventory report; and (4) require recordkeeping and reporting of
pesticide usage. EPA also proposes to approve CDPR's commitments to
manage VOC emissions from the use of agricultural and commercial
structural pesticides in the SJV to ensure that they do not exceed 18.1
tons per day and to implement restrictions on VOC emissions in the SJV
from non-fumigant pesticides by 2014. Lastly, EPA is providing its
response to a remand by the Ninth Circuit Court of Appeals of EPA's
2009 approval of a revision to the California SIP related to reducing
VOC emissions from pesticides.
DATES: Any comments must arrive by May 24, 2012.
ADDRESSES: Submit comments, identified by docket number EPA-R09-OAR-
2012-0194, by one of the following methods:
Federal eRulemaking Portal: www.regulations.gov. Follow
the on-line instructions.
Email: steckel.andrew@epa.gov.
Mail or deliver: Andrew Steckel, (AIR-4), U.S.
Environmental Protection Agency Region 9, 75 Hawthorne Street, San
Francisco, CA 94105.
Instructions: All comments will be included in the public docket
without change and may be made available online at www.regulations.gov,
including any personal information provided, unless the comment
includes Confidential Business Information (CBI) or other information
whose disclosure is restricted by statute. Information that you
consider CBI or otherwise protected should be clearly identified as
such and should not be submitted through www.regulations.gov or email.
The www.regulations.gov Web site is an ``anonymous access'' system, and
EPA will not know your identity or contact information unless you
provide it in the body of your comment. If you send email directly to
EPA, your email address will be automatically captured and included as
part of the public comment. If EPA cannot read your comments due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment.
Docket: The technical support document (TSD) and the index to the
docket for this proposed action is available electronically on the
www.regulations.gov Web site and in hard copy at EPA Region 9, 75
Hawthorne Street, San Francisco, California 94105. While all documents
in the docket are listed in the index, some information may be publicly
available only at the hard copy location (e.g., copyrighted material),
and some may not be publicly available at either location (e.g., CBI).
To inspect the hard copy materials, please schedule an appointment
during normal business hours with either of the contacts listed in the
FOR FURTHER INFORMATION CONTACT section below.
FOR FURTHER INFORMATION CONTACT: For information on the proposed action
on CDPR's regulations: Nancy Levin, Rules Office (AIR-4), (415) 972-
3848, levin.nancy@epa.gov. For information on the proposed actions on
CDPR's commitments and the PEST-1 measure: Frances Wicher, Air Planning
Office (AIR-2), (415) 972-3957, wicher.frances@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, ``we'', ``us'' and
``our'' refer to EPA.
Table of Contents
I. Introduction
II. The Current California SIP Pesticide Element and Description of
the Proposed Revisions
A. Currently-Approved Provisions of the California SIP Pesticide
Element
B. Proposed Revisions to the California SIP Pesticide Element
III. EPA's Evaluation of the Revisions to the California SIP
Pesticide Element
A. Clean Air Act (CAA) Procedural and Administrative
Requirements for SIP Submittals Under CAA Section 110
[[Page 24442]]
B. Enforceability of Emission Limitations Under CAA Section
110(a)(2)(A)
C. Reasonably Available Control Measures/Reasonably Available
Control Technology (RACM/RACT) Requirement Under CAA Sections
172(c)(1) and 182(b)(1)
D. Finding of Non-Interference With Applicable Requirements of
the CAA Under Section 110(l)
IV. Response To Remand in Association of Irritated Residents Case
V. Proposed Actions and Opportunity for Public Comment
VI. Statutory and Executive Order Reviews
I. Introduction
This proposed action deals with revisions to California's
federally-approved program to reduce emissions from the use of
agricultural and structural pesticides to improve ozone air quality in
five areas of the State: the South Coast, Southeast Desert (SED),
Ventura, San Joaquin Valley (SJV), and Sacramento Metro nonattainment
areas. Pesticides contribute to ozone pollution through the emissions
of volatile organic compounds (VOC). VOC react in the atmosphere with
nitrogen oxides (NOX) in the presence of sunlight to form
ozone. Breathing ground-level ozone can result in a number of health
effects that are observed in broad segments of the population. These
health effects include reduced lung function and inflamed airways,
which can increase respiratory symptoms and aggravate asthma or other
lung diseases. Ozone exposure also has been associated with increased
susceptibility to respiratory infections, medication use, doctor
visits, and emergency department visits and hospital admissions for
individuals with lung disease. Ozone exposure also increases the risk
of premature death from heart or lung disease. Children are at
increased risk from exposure to ozone because their lungs are still
developing and they are more likely to be active outdoors, which
increases their exposure.
Pesticides contribute about 5 percent to total VOC emissions in SJV
and Ventura ozone nonattainment areas and less than 1 percent to total
VOC emissions in the South Coast, SED, and Sacramento Metro areas. See
TSD, section I.D.
This proposal addresses the regulation of VOC emissions from
pesticides under the federal Clean Air Act (CAA or ``Act''). Pesticides
and their uses and application are primarily regulated under Federal
Insecticide, Fungicide, and Rodenticide Act (FIFRA). This proposal does
not address regulations of pesticides under FIFRA or other federal
acts.
II. The Current California SIP Pesticide Element and a Description of
the Proposed Revisions
A. Currently-Approved Provisions of the California SIP Pesticide
Element
Prior to today's proposal, EPA has taken three actions to either
approve or revise provisions of the California SIP Pesticide Element.
We briefly describe each action below. More information on each action
and its background can be found in section I.E. of the TSD for this
proposal.
1994 Pesticide Element--The 1994 Pesticide Element was
submitted by California in November 1994 as part of the State's
comprehensive 1-hour ozone attainment plan (known as the 1994 Ozone
SIP) and included a plan by CDPR to reduce VOC emissions from
agricultural and structural pesticides in five ozone nonattainment
areas by a maximum of 20 percent from 1990 baseline levels by 2005 and
to adopt regulations if necessary to achieve these reductions. EPA
approved the 1994 Pesticide Element on January 8, 1997 (62 FR 1150) and
codified it at 40 CFR 52.220(c)(204)(i)(A)(6) and 52.220(c)(236).
PEST-1 Measure in CARB's 2003 State Strategy--In 2003, the
California Air Resources Board (CARB) updated the statewide strategy
that was part of the 1994 Ozone SIP. One of the measures in the 2003
State Strategy was PEST-1 (``Implement Existing Pesticide Strategy''),
which retained and continued unchanged the provisions of the 1994
Pesticide Element. EPA approved the PEST-1 measure into the California
SIP as part of its action to approve in part and disapprove in part the
2003 South Coast Air Quality Management Plan and 2003 State Strategy.
See 74 FR 10176 (March 10, 2009), codified at 40 CFR
52.220(c)(339)(ii)(A)(1).\1\
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\1\ In Association of Irritated Residents v. EPA, No. 09-71383,
the 9th Circuit Court of Appeals remanded the approval of PEST-1 to
EPA with the instructions to determine whether the Pesticide Element
has sufficient enforcement mechanisms to satisfy the requirements of
the Clean Air Act (CAA or Act). We provide our response to the
remand in section IV of this notice.
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2007 Ventura Pesticide Element--In 2007, CARB submitted a
revision to the Ventura portion of the 1994 Pesticide Element. This
revision reduced in part and temporally the emissions reduction
commitment for Ventura in 1994 Pesticide Element. EPA approved this
revision in 2008. See 73 FR 41277 (July 18, 2008), codified at 40 CFR
52.220(c)(355)(i)(A).
B. Proposed Revisions to the California SIP Pesticide Element
EPA is proposing to approve regulations and commitments adopted by
the CDPR to limit VOC emissions from the use of agricultural and
commercial structural pesticides in the South Coast, SED, Ventura, SJV,
and Sacramento Metro ozone nonattainment areas.\2\ These CDPR
regulations and commitments were submitted by CARB to EPA as follows:
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\2\ The South Coast nonattainment area includes Orange County
and portions of Los Angeles, San Bernardino, and Riverside Counties.
The Southeast Desert (SED) nonattainment area includes the Coachella
Valley in Riverside County, Antelope Valley in Los Angeles County,
and the southwestern quadrant of San Bernardino County. The Ventura
nonattainment area is Ventura County. The San Joaquin Valley (SJV)
nonattainment area includes San Joaquin, Stanislaus, Merced, Madera,
Fresno, Tulare and Kings Counties and the valley portion of Kern
County. The Sacramento Metro nonattainment area includes Sacramento
County and parts of El Dorado, Placer, Solano and Sutter Counties.
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1. October 12, 2009 submittal \3\ of the following CDPR
regulations:
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\3\ See letter, James N. Goldstene, Executive Officer, CARB to
Laura Yoshii, Acting Regional Administrator, EPA Region 9, October
12, 2009.
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Title 3 California Code of Regulations (CCR), sections
6447 (first paragraph) and 6447.3-6452 pertaining to field fumigation
methods;
Portions of 3 CCR sections 6452.1-6452.4 and sections
6624-6626 pertaining to emission inventory;
3 CCR sections 6452.2 and 6452.3 pertaining to field
fumigation limits and allowances in the Ventura ozone nonattainment
area.\4\
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\4\ CARB did not submit for inclusion into the SIP those
portions of 3 CCR sections 6452.2 and 6452.3 pertaining to field
fumigation limits and allowances in the South Coast, SED, SJV, and
Sacramento Metro ozone nonattainment areas.
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2. October 12, 2009 submittal \5\ of CDPR's revised ``Pesticide
Emission Reduction Commitment for the San Joaquin Valley''. This
submittal caps VOC emissions from the use of agricultural and
commercial structural pesticides in the SJV to 18.1 tpd and commits
CDPR to implement restrictions on non-fumigant pesticides in the SJV by
2014.
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\5\ See letter, James N. Goldstene, Executive Officer, CARB to
Laura Yoshii, Acting Regional Administrator, EPA Region 9, October
12, 2009.
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3. August 2, 2011 submittal \6\ of the following CDPR regulations
which revised in part and added to the October 12, 2009 submittal: \7\
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\6\ See letter, James N. Goldstene, Executive Officer, CARB to
Jared Blumenfeld, Regional Administrator, EPA Region 9, August 2,
2011.
\7\ As part of its August 2, 2011 submittal, CARB also submitted
3 CCR section 6400 (Restricted Materials), 6446 (Methyl Iodide
Field--General Requirements) and section 6446.1 (Methyl Iodide Field
Fumigation Methods) and methyl-iodide related portions of provisions
6452.2(a)(4)(Annual Volatile Organic Compound Emissions Inventory
Report) and 6624(f) (Pesticide Use Records). We are deferring action
on these provisions due to California's cancellation, effective
March 21, 2012, of the registration of all products containing the
active ingredient methyl iodide. CDPR adopted this set of methyl
iodide-related regulations on May 11, 2011, after and separately
from the CDPR April 7, 2011 regulations that are also included in
the CARB August 2, 2011 submittal.
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[[Page 24443]]
3 CCR sections 6448.1, 6449.1, and 6450.1 pertaining to
fumigation method restrictions.
Portions of 3 CCR sections 6452.2 and 6452.3 pertaining to
field fumigation limits and allowances in the Ventura ozone
nonattainment area.
3 CCR section 6452.4 pertaining to the annual VOC
emissions inventory report.
3 CCR sections 6624 and 6626 pertaining to pesticide use
records and reports.
The submitted CDPR regulations that we are proposing action on
today can be divided into four distinct but related parts. The first
part (3 CCR sections 6447 through 6452) establishes standards for
fumigant application and restricts the use of certain higher-emitting
application methods in the five nonattainment areas. The second part (3
CCR sections 6452.2 and 6452.3) provides a contingency mechanism to
limit VOC emissions from field fumigant applications in the Ventura
nonattainment area. The third part (3 CCR section 6452.4) requires CDPR
to annually report on pesticide VOC emissions in each of the five
nonattainment areas and establishes requirements for the report. The
fourth part (3 CCR sections 6624 and 6626) establishes the
recordkeeping and reporting requirements necessary to ensure compliance
with the other parts. We describe each part in more detail below.
The first part (3 CCR sections 6447 through 6452) establishes, by
fumigant and method, requirements for the field application of seven
fumigants and restricts the use of certain higher-emitting application
methods in the South Coast, SED, Ventura, SJV, and Sacramento Metro
ozone nonattainment areas during the period May 1 to October 31.\8\
Requirements are described for the field fumigants: methyl bromide
(sections 6447 and 6447.3), 1,3-dichloropropene (sections 6448 and
6448.1), chloropicrin (sections 6449 and 6449.1), metam-sodium,
potassium N-methyldithiocarbamate and dazomet (sections 6450, 6450.1
and 6450.2), and sodium tetrathiocarbonate (sections 6451 and 6451.1).
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\8\ CDPR's regulations establishing the parameters for field
fumigant application methods (but not the restrictions on which
methods may be used during certain periods of the year) apply
statewide; however, EPA is limiting its approval to just the five
listed nonattainment areas.
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Specific requirements for applying these fumigants include, for
example, limiting fumigant application rates (pounds/acre); specifying
application methods (e.g., minimum injection depth below soil surface,
number of water treatments, minimum hours to leave tarpaulin in place);
and requiring plans to address damaged tarpaulins. 3 CCR section 6452
allows CDPR to approve alternative fumigation methods under certain
conditions and based on specific criteria.
As submitted, the second part of CDPR's regulations (3 CCR sections
6452.2 and 6452.3) apply only to the Ventura ozone nonattainment area.
This part requires CDPR to set a field fumigant VOC emissions limit for
Ventura in its annual VOC emissions inventory report if overall
pesticide emissions (not just fumigant emissions) in the Ventura
nonattainment area are found to be within five percent of or exceed the
listed benchmark. The benchmark is equivalent to the 20 percent
reduction in pesticide VOC emissions from 1990 emissions levels that is
required in the area by the California SIP Pesticide Element. This part
further requires that the county agricultural commissioner add
conditions to field fumigation permits or take other actions that will
prevent the field fumigant limit from being exceeded.
The third part of the submitted regulations (3 CCR section 6452.4)
requires CDPR to issue an annual emissions inventory report that
reports the total agricultural and commercial structural (fumigant and
nonfumigant) pesticide VOC emissions for previous years in each of the
five nonattainment areas and evaluates compliance with the emissions
reduction targets in each area. This section specifies the method for
calculating emissions and requires CDPR make a draft emissions
inventory available to the public for a 45-day comment period and post
the final report on its Web site.
The fourth part of the submitted regulations (3 CCR sections 6624
and 6626) establishes the pesticide use recordkeeping and reporting
requirements needed to assure compliance with the other parts. This
part requires anyone using pesticides in specific applications to keep
and maintain certain records for two years and requires operators of
property that produces an agricultural commodity and agricultural pest
control businesses to report the use of pesticides to the county
agricultural commissioner. These sections require the recording and
reporting of the method for fumigant application in the five
nonattainment areas.
CDPR has revised its commitments in the 1994 Pesticide Element to
limit VOC emissions from agricultural and commercial structural
pesticides in the SJV. Specifically, it is now committing to
Use a specified emissions estimation methodology to
establish the 1990 pesticide VOC emission levels and evaluate
compliance with the provisions in the 1994 Pesticide Element for SJV;
Implement restrictions on agricultural fumigation methods
and by 2014 implement restrictions on VOC emissions from non-fumigant
pesticides; and
Manage VOC emissions from agricultural and commercial
structural pesticide use to ensure that they do not exceed 18.1 tons-
per-day in the SJV area (which is equivalent to a 12 percent reduction
in pesticide VOC emissions from 1990 levels).
III. EPA's Evaluation of the Revisions to the California SIP Pesticide
Element
A. CAA Procedural and Administrative Requirements for SIP Submittals
Under CAA Section 110
CAA sections 110(a)(1) and (2) and 110(l) require a state to
provide reasonable public notice and opportunity for public hearing
prior to the adoption and submittal 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 EPA's implementing regulations in
40 CFR 51.102. All three submittals under consideration here included
evidence of adequate public notice and opportunity for comment.
CAA section 110(k)(1)(B) requires EPA to determine whether a SIP
submittal is complete within 60 days of receipt. This section also
provides that any SIP submittal that we have not affirmatively
determined to be complete or incomplete will become complete by
operation of law six months after the day of submittal. The October 12,
2009 submittals of the CDPR's regulations and the revised SJV Pesticide
Element went complete by operation of law on April 12, 2009. The August
2, 2011 submittal of revisions to CDPR's regulations went complete by
operation of law on February 2, 2012.
[[Page 24444]]
B. Enforceability of Emission Limitations Under CAA Section
110(a)(2)(A)
CAA section 110(a)(2)(A) requires that SIP ``shall include
enforceable emissions limitations, and such other control measures,
means or techniques (* * *) as well as schedules and timetables for
compliance, as may be necessary or appropriate for attainment * * *.''
In order to be enforceable, SIP regulations and commitments must be
clear regarding, for example, who must comply, by what date, the
standard of compliance, the methods used to determine compliance, and
the process and criteria for obtaining any variation from the normal
mode of compliance.\9\ Guidance used to help evaluate enforceability
includes the Bluebook and the Little Bluebook.\10\
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\9\ ``Review of State Implementations Plans and Revisions for
Enforceability and Legal Sufficiency'' (Enforceability Guidance),
Craig Potter, EPA, September 23, 1987. See also General Preamble for
the Implementation of Title I of the Clean Air Act Amendments of
1990. 57 FR 13498, 13502 and 13541 (April 16, 1992) and CAA sections
110(a)(2) and 172(c)(6). https://www.epa.gov/compliance/resources/policies/civil/caa/stationary/review-enf-rpt.pdf.
\10\ ``Issues Relating to VOC Regulation Cutpoints,
Deficiencies, and Deviations,'' U.S. EPA, OAQPS, May 25, 1988 (``the
Bluebook'') and ``Guidance Document for Correcting Common VOC and
Other Rule Deficiencies,'' U.S. EPA Region 9, August 21, 2001 (``the
Little Bluebook'').
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Field Fumigant Regulations
CDPR's regulations include recordkeeping requirements in 3 CCR
section 6624 (Pesticide Use Records) and the reporting requirements in
3 CCR section 6626 (Pesticide Use Reports for Production Agriculture).
Among these recordkeeping and reporting requirements is the provision
that require any person who uses a fumigant in any of the five ozone
nonattainment areas to record and report a description of the
application method. See 3 CCR sections 6624(f) and 6626(d). The
regulations provide specific methods, limits, and timeframes for
agricultural use of each fumigant. The regulations provide a process
and criteria for use of a field fumigation method not described in the
regulations. The request to implement a method not described in the
regulations must be accompanied by scientific data documenting the VOC
emissions, and that the method will not result in emissions greater
than any one of the methods allowed for use by the regulations. The
director must consider criteria such as data sufficiency and validity,
and representativeness of field conditions studied. See 3 CCR section
6452.
The recordkeeping and report requirements and other rule provisions
in the submitted regulations are clear and adequate to ensure that
California's submitted fumigant regulations is enforceable as required
by of CAA section 110(a)(2)(A).
Pesticide Emission Reduction Commitment for the San Joaquin Valley
The mechanism to track compliance with the 18.1 tpd limit on VOC
emissions from agricultural and commercial structural pesticides in SJV
is the Annual VOC Emissions Inventory Report required by 3 CCR section
6452.4. (Annual Volatile Organic Compound Emissions Inventory Report).
For tracking compliance with the overall VOC limit in the SJV, CDPR
proposes to use the emissions estimation methodology described on page
2-4 (in the section ``Procedure for Calculating Unadjusted and Adjusted
Volatile Organic Compound Emissions'') of November 5, 2008 memorandum
from Rosemary Neal, CDPR to Randy Segawa, CDPR, Subject: Update to the
Pesticide Volatile Organic Inventory; Estimated Emissions 1990-2006,
and Preliminary Estimates for 2007 (``Neal memorandum'').\11\
Procedures for calculating pesticide VOC emissions are also in 3 CCR
section 6452.4(a)(1).\12\ The Neal memorandum lays out a calculation
process that follows standard inventorying practice and provides the
same procedures for calculating VOC emissions as 3 CCR section
6452.4(a)(1). Pesticide usage rates used to calculate total emissions
are collected from pesticide use reports which are required by 3 CCR
section 6626 and the requirements for persons (e.g., pesticide
applicators) to keep and report the data necessary for preparing the
annual report are in 3 CCR section 6624. These provisions are clear and
adequate in combination with the fumigant regulations to ensure the
pesticide VOC limit for the SJV is enforceable as required by CAA
section 110(a)(2)(A).
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\11\ The Neal memorandum was included as part of October 12,
2009 submittal of the ``Pesticide Emission Reduction Commitment for
the San Joaquin Valley'' and we intend to include it as additional
material in the California SIP should we finalize our proposed
approval of CDPR's commitment.
\12\ These procedures apply not only to SJV but also to the
other four nonattainment areas.
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CDPR has committed to implement restrictions on VOC emissions from
non-fumigant regulations by 2014 which we interpret to mean by no later
than May 1, 2014 given that CDPR projects emissions reductions from
these restrictions in 2014 and its control program operates from May 1
to October 31 of each year. See ``Proposed SIP Commitment for San
Joaquin Valley,'' page 2. To achieve reductions in 2014, the
restriction would need to be implemented by the beginning of the
regulatory season (May 1) in that year. CDPR does not commit to a
specific emissions reduction from the additional restrictions on non-
fumigant pesticide; however, the restrictions are part of CDPR's
regulatory program to ensure that the inventory target of 18.1 tpd in
the SJV is not exceeded (Id. at page 1), which effectively defines the
needed stringency. This commitment is sufficiently clear and adequate
to ensure that is enforceable as required by CAA section 110(a)(1)(A).
C. Reasonably Available Control Measures/Reasonably Available Control
Technology (RACM/RACT) Requirement Under CAA Sections 172(c)(1) and
182(b)(1)
CAA section 172(c)(1) requires that each attainment plan ``provide
for the implementation of all reasonably available control measures as
expeditiously as practicable (including such reductions in emissions
from existing sources in the area as may be obtained through the
adoption, at a minimum, of reasonably available control technology),
and shall provide for attainment of the national primary ambient air
quality standards.'' RACM is a requirement only for nonattainment
areas.
EPA defines RACM as any potential control measure for application
to point, area, on-road and non-road emissions source categories that
meets certain criteria. These criteria include whether the measure is
technologically and economically feasible and either individually or
collectively with other RACM can advance the attainment date by at
least one year. See 57 FR 13498, 13560 (April 16, 1992). The
determination as to whether a SIP provides for the implementation of
RACM as required by CAA section 172(c)(1) is done as part of an area's
attainment and reasonable further progress plans and not on a rule-by-
rule basis.
For ozone nonattainment areas classified as moderate or above, CAA
section 182(b)(2) requires the implementation of reasonably available
control technologies (RACT) on all major sources of VOC \13\ and for
each
[[Page 24445]]
VOC source category for which EPA has issued a Control Techniques
Guideline (CTG). CAA section 182(f) requires that RACT under section
182(b)(2) also apply to major stationary sources of NOX. See
CAA sections 182(d) and (f).
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\13\ In areas classified as severe (such as SED, Ventura, and
Sacramento Metro), a major source is a stationary source that emits
or has the potential to emit at least 25 tons of VOC or
NOX per year. See CAA sections 182(d) and (f). For
extreme areas (South Coast and SJV), a major stationary sources is
one that emits or has the potential to emit at least 10 tons of VOC
or NOX per year. See CAA sections 182(e) and (f).
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The proposed revisions to the California SIP Pesticide Element that
we are evaluating here are intended to reduce VOC emissions in the
South Coast, SED, Ventura, SJV, and Sacramento Metro ozone
nonattainment areas. VOC emissions contribute to the formation of ozone
and secondary particulate matter. EPA, though, has determined by rule
that states do not need to address controls for sources of VOC
emissions for PM2.5 standard attainment unless the state
and/or EPA make a technical demonstration that such controls would
significantly contribute to reducing PM2.5 concentrations in
the nonattainment area. See 40 CFR 51.1002(c)(3). Such a determination
would be made in the context of each area's plan for attainment of the
PM2.5 standards. Of the areas subject to the California SIP
Pesticide Element, only the South Coast, SJV, and Sacramento Metro
areas are nonattainment for one or more of the PM2.5
standards and only South Coast controls VOC for PM2.5
attainment.
Field Fumigant Regulations
CARB's 2009 submittal of the field fumigant regulations did not
include a demonstration of how the field fumigation methods implement
RACT.\14\ In response to EPA comments, CDPR provided a document
containing more detailed information on its RACT evaluation of
fumigation methods.\15\ This document contains a general discussion of
strategies for controlling VOC emissions from fumigants and an
evaluation of field fumigation method options, including the basis for
those accepted and those rejected by CDPR for inclusion in its
regulations. It discusses current research on fumigant VOC emission
reduction methods, including a reevaluation of fumigants to obtain
additional data to replace surrogate data used in developing the
adopted regulations.
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\14\ See letter, Andrew Steckel, EPA Region 9 to Frank Spurlock,
CDPR and Mike Guzzetta, CARB, November 2, 2010.
\15\ See letter and attachments, Randy Segawa, CDPR to Andrew
Steckel, EPA-Region 9, Reducing Volatile Organic Compound Emissions
from Pesticides: Analysis of Alternatives for Field Fumigation
Methods, June 28, 2011.
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Field fumigation emissions are considered fugitive emissions
because they are emissions that ``could not reasonably pass through a
stack, chimney, vent, or other functionally-equivalent opening.'' \16\
As noted above, CAA section 182(b)(1) requires RACT be applied to all
to major stationary sources in a ozone nonattainment area classified
moderate or above. EPA has not yet defined by rule whether fugitive
emissions must be included in determination of major source status for
the purposes determining the application of section 182(b)(1) RACT
requirement; however, EPA believes, based on the information provided
in the CDPR's alternatives analysis, and the research cited to support
it, that CDPR has demonstrated that the proposed regulations are
stringent enough to implement RACT-level controls on the application of
pesticides.
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\16\ See 40 CFR 70.2 (Definitions).
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On January 10, 2012, EPA partially approved and partially
disapproved the section 182(b)(1) RACT SIP submitted by California on
June 18, 2009 for the SJV ozone nonattainment area. The partial
disapproval was based in part on our conclusion that the State had not
fully satisfied CAA section 182(b) RACT requirements for the
application of fumigants. See 77 FR 1417, 1425 (January 10, 2012).
Based on our proposed finding here that CDPR's field fumigant
regulations provide RACT-level controls on this source category, final
approval of these regulations would satisfy California's obligation to
implement RACT under CAA section 182(b)(1) for this source category for
the 1-hour ozone and 1997 8-hour ozone standards for the SJV RACT SIP.
EPA has recently approved the attainment, RFP and RACM
demonstrations in the 8-hour ozone SIPs for the South Coast and San
Joaquin Valley and the PM2.5 SIP for the South Coast (which
did include VOC reductions in its RFP and attainment
demonstrations).\17\ These demonstrations relied in part on VOC control
measures in the 2007 State Strategy; however, EPA's approval of these
demonstrations did not rely on emissions reductions from CDPR's field
fumigant regulations. Therefore, their approval into the SIP is
consistent with the approved RACM demonstrations.
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\17\ See 76 FR 69928 (November 9, 2011) (South Coast
PM2.5 Plan), 77 FR 12652 (March 1, 2012) (SJV 2007 8-hour
Ozone SIP), and 77 FR 12674 (March 1, 2012) (South Coast 8-hour
Ozone Plan). EPA has also recently approved the SJV 2008
PM2.5 SIP which relied in part on measures in the 2007
State Strategy. In approving that SIP, EPA concurred with the
State's determination that VOC did not need to be controlled for
PM2.5 attainment in the SJV and therefore the plan did
not include did not need to evaluate VOC control measures as part of
its RACM demonstration. See 76 FR 69896, 69924 (November 9, 2011).
The PM2.5 plan for the Sacramento Metro area is not due
until late 2012.
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CARB has submitted SIPs to address attainment of the 1997 8-hour
ozone standard in the SED, Ventura County, and Sacramento Metro
nonattainment. EPA has not yet acted on these plans although we note
that none rely on reductions from controls on pesticides.
Pesticide Emission Reduction Commitment for the San Joaquin Valley
As noted above, the demonstration that a SIP provides for the
implementation of RACM as required by CAA section 172(c)(1) is done as
part of an area's attainment and reasonable further progress plans and
not on an individual rule or commitment basis.
EPA recently approved the 2007 8-hour ozone SIP for the San Joaquin
Valley, including the SIP's RACM demonstration. 77 FR 12652 (March 1,
2012). To demonstrate that the SIP provided for RACM, California relied
in part on measures in the 2007 State Strategy, including the
``Pesticide Emission Reduction Commitment for the San Joaquin Valley''
(as revised April 17, 2009) that we are proposing to approve here.
However, because we had not yet approved the commitment into the SIP,
we did not grant any emissions reductions credit to the commitment in
either the RFP or attainment demonstration nor did we rely on it to
make our determination that the 2007 SIP provided for RACM. See Air
Division, EPA Region 9, ``Final Technical Support Document and Response
to Comments Final Rule on the San Joaquin Valley 2007 Ozone Plan and
the San Joaquin Valley Portions of the 2007 State Strategy,'' December
15, 2011, pp. 51-57. Because EPA's approvals of the attainment, RFP,
and RACM demonstrations in the SJV 2007 8-hour ozone SIP did not rely
on emissions reductions from CDPR's commitment to limit pesticide VOC
emissions in the SJV to 18.1 tpd, its approval into the SIP is
consistent with the approved RACM demonstration.
D. Finding of Non-Interference With Applicable Requirements of the CAA
Under Section 110(l)
Revisions to the SIP, including revisions to SIP-approved control
measure, must meet the requirements of CAA section 110(l) to be
approved by EPA. CAA section 110(l) ``Plan Revisions'' provides in
relevant part:
The Administrator shall not approve a revision of a plan if the
revision would interfere with any applicable requirement concerning
attainment and reasonable further progress (as defined in [section
171]) or any other applicable requirement of [the CAA].
[[Page 24446]]
We interpret section 110(l) to apply to all requirements of the CAA
and to all areas of the country, whether attainment, nonattainment,
unclassifiable, or maintenance for one or more of the six criteria
pollutants. We also interpret section 110(l) to require a demonstration
addressing all pollutants whose emissions and/or ambient concentrations
may change as a result of the SIP revision. The scope and rigor of an
adequate section 110(l) demonstration of noninterference depends on the
air quality status of the area, the potential impact of the revision on
air quality, the pollutant(s) affected, and the nature of the
applicable CAA requirements.
In reviewing a modification to an approved SIP provision, we look
to see to what extent the existing SIP has relied on that provision to
meet applicable CAA requirements. For emissions reduction measures, we
generally conclude that the revision will not interfere with any
applicable requirement related to attainment or RFP if the revised SIP
will provide the same or more emissions reductions on the same or
similar schedule as the existing SIP. We note, however, that CAA
section 110(l) does not bar approval of SIP revisions that may result
in higher levels of emissions than would potentially occur under the
unrevised SIP; only that such revisions do not result in the applicable
SIP no longer providing for expeditious attainment or RFP or complying
with any other applicable requirements of the CAA.
The submittals that we are evaluating in this proposal for
inclusion into the California SIP control VOC emissions in five
California areas. Neither the field fumigant regulations nor the SJV
pesticide SIP commitment explicitly regulated any other pollutant
besides VOC. VOC is a precursor pollutant for ozone as well as for both
fine (PM2.5) and coarse (PM10) particulate
matter.\18\ At this time, only the South Coast's SIP relies on VOC
controls for PM2.5 or PM10 attainment and none of
its adopted particulate matter plans rely on reductions from the
California SIP Pesticide Element (either as already approved or
proposed for approval here) to demonstrate attainment, RFP, or RACM or
to meet any other requirement of the CAA.
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\18\ As noted previously, while EPA considers VOC to be a
precursor to PM, it does not require control of VOC emissions for PM
standard attainment in most instances. See 72 FR 20586, 20589 (April
25, 2007) and 57 FR 13498, 13538 (April 16, 1992).
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Field Fumigant Regulations
The CDPR's field fumigant regulations are the first such
regulations incorporated into the California SIP. Their approval will
strengthen the SIP by providing SIP-enforceable measures and compliance
procedures to reduce emissions from the application of fumigants in the
five ozone nonattainment areas covered by the regulations. Their
approval will also aid compliance with the approved California SIP
Pesticide Element's provisions for reducing VOC emissions by 20 percent
from 1990 baseline levels in the South Coast, SED, Ventura, and
Sacramento Metro ozone nonattainment areas. Their approval will also
aid compliance with the proposed 18.1 tpd limit on pesticide VOC
emissions in the San Joaquin Valley. Therefore, EPA proposes to find
that approving the field fumigant regulations into the California SIP
will not interfere with any applicable requirement concerning
attainment and reasonable further progress or with any other applicable
requirement of the CAA.
Pesticide Emission Reduction Commitment for the San Joaquin Valley
In 1997, EPA approved the 1994 Pesticide Element into the
California SIP. See 62 FR 1150, 1170 (January 8, 1997). As approved,
the Element's goal was to reduce VOC emissions from agricultural and
commercial structural pesticide applications by a maximum of 20 percent
from the 1990 baseline emission inventory by 2005 in areas that relied
on VOC reductions from pesticides in their attainments plans with
reductions to occur linearly from 1990 to 2005 but it allowed for less
than 20 percent if fewer VOC reductions from pesticide were needed. See
``The State Implementation Plan for Agricultural and Commercial
Structural Pesticides,'' November 15, 1994 (``1994 Pesticide SIP''), p.
1.\19\
---------------------------------------------------------------------------
\19\ As submitted, the 1994 Pesticide Element consisted of three
documents: the 1994 Pesticide SIP and the memorandum from James W.
Wells, Director, CDPR, to James D. Boyd, Executive Officer, CARB,
May 9, 1995 (``Wells memorandum'') and the letter from James D.
Boyd, Executive Officer, CARB, to David Howekamp, Division Director,
EPA-Region 9, June 13, 1996 (``Boyd Letter''). As approved, it
consisted of the 1994 Pesticide SIP (40 CFR 52.220(c)(204)(i)(A)(6))
and the Boyd letter (40 CFR 52.220(c)(236)). See section IV of this
preamble for further discussion of the 1994 Pesticide Element.
---------------------------------------------------------------------------
The attainment demonstration for the SJV in the 1994 Ozone SIP
relied in part on reductions of 12 percent from 1990 emissions levels
from the 1994 Pesticide Element to demonstrate attainment by the area's
then-applicable attainment deadline of November 15, 1999. In approving
the 1994 Pesticide Element and the SJV ozone attainment demonstration,
EPA credited the element with 13 tpd (in 1994 SIP currency \20\) in VOC
emissions reductions in 1999.\21\ At the same time, EPA noted that
California had committed to adopt and submit any regulations necessary
to reduce VOC emissions from agricultural and commercial structural
pesticides by 12 percent in 1999 \22\ in SJV. See 61 FR 10920, 10935
(March 18, 1996).
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\20\ A SIP's ``currency'' is the emissions inventory on which it
is based. An emissions reduction expressed in a particular ``SIP
currency'' is an emissions reduction calculated using the inventory
included in that SIP. Because inventories vary from SIP to SIP for
reasons unrelated to controls (e.g., improved activity estimates or
emissions factors), the estimated emissions reductions from a
control measure in tons per day can change from SIP to SIP even if
the effectiveness of the control measure as a percentage of the
emissions category does not.
\21\ The 13 tpd figure was provided by CARB on page A-2 and in
Attachment C of the Boyd Letter. For the 1994 Ozone SIP, the State
estimated that VOC emissions from pesticide use in 1990 in the San
Joaquin Valley were 62.5 tpd. A 12 percent reduction from this level
would require reducing overall pesticide emissions to be no more
than 55.0 tpd in 1999. The State further estimated that without
controls, VOC emissions from pesticides in the SJV would increase to
67.9 tpd by 1999, thereby requiring a reduction of 12.9 tpd (67.9
tpd minus 55.0 tpd, rounded to 13 tpd) in 1999 in order to meet the
target level for a 12 percent reduction. See CDPR, Staff Report on
the Department of Pesticide Regulation's Proposed SIP Commitment for
San Joaquin Valley,'' undated, p. 1, ftn 1.
\22\ A 20 percent reduction that was to occur linearly over the
fifteen years between 1990 and 2005 would accrue reductions at a
rate of 1.33 percent per year (20 percent divided by 15 years)
resulting in a 12 percent reduction by 1999 (9 years times 1.33
percent per year).
---------------------------------------------------------------------------
In 2003, CARB updated the strategy that was part of the 1994 Ozone
SIP. One of the measures in the 2003 State Strategy was PEST-1
(``Implement Existing Pesticide Strategy''), which retained the
provisions of the 1994 Pesticide Element. In 2004, CARB submitted the
2004 Extreme [1-hour Ozone] Attainment Plan for the SJV \23\ which
relied in part on the 2003 State Strategy for the reductions needed to
demonstrate attainment by SJV's new applicable attainment date of
November 15, 2010. On page 27 of its staff report for that plan,\24\
CARB discusses the measures in the 2003 State Strategy including PEST-
1. It describes the measure as a ``[c]ontinuation of the Department of
Pesticide Regulation's approved SIP obligation to reduce volatile
emissions from pesticides [which f]or the San Joaquin Valley * * *
means a pesticide VOC emissions
[[Page 24447]]
target of 12 percent less than 1990 levels.''
---------------------------------------------------------------------------
\23\ San Joaquin Valley Air Pollution Control District,
``Extreme Ozone Attainment Demonstration Plan'' adopted October 8,
2004; amended October 20, 2005 and August 21, 2008.
\24\ CARB, Staff Report, Proposed 2004 State Implementation Plan
For Ozone In The San Joaquin Valley, Release Date: September 28,
2004.
---------------------------------------------------------------------------
EPA approved PEST-1 into the SIP as part of its action to approve
in part and disapprove in part the 2003 South Coast AQMP. See 74 FR
10176 (March 10, 2009), codified at 40 CFR 52.220(c)(ii)(A)(1). We have
not approved any other changes to the SJV-related provisions of 1994
Pesticide Element nor have we granted any emissions reductions credit
for the 1994 Pesticide Element beyond the 13 tpd (in 1994 SIP currency)
approved as part of our action on the 1994 Ozone SIP.\25\
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\25\ We have approved two ozone plans for the SJV since the
1997: the 2004 Ozone Plan in 2010 and the second, the 2007 8-hour
Ozone Plan in 2012. See 75 FR 10420 (March 8, 2010) and 77 FR 12652
(March 1, 2012). Neither plan nor our approval of them relied on
reductions in pesticide emissions to meet any applicable CAA
requirement.
---------------------------------------------------------------------------
California is now proposing to revise its SIP Pesticide Element for
the SJV to replace the requirement to achieve a percent reduction in
VOC emissions from pesticides with a limit on overall VOC emissions
from pesticides in the SJV of 18.1 tpd of VOC during the high ozone
season of May 1 to October 31. The 18.1 tpd cap equates to a reduction
of 12 percent from the current estimate of 1990 pesticide VOC emissions
levels in the SJV.\26\
---------------------------------------------------------------------------
\26\ See CDPR, Staff Report on the Department of Pesticide
Regulation's Proposed SIP Commitment for San Joaquin Valley,''
undated (enclosure 2 to memorandum, Christopher W. Reardon, Chief
Deputy Director, CDPR, to James Goldstene, Executive Officer, CARB,
October 5, 2009; subject: Amendments to the Pesticide Element of the
Ozone State Implementation Plan).
---------------------------------------------------------------------------
Based on our review of the proposed revision, we find that the
revision will result in, at minimum, the same emissions reductions that
are currently required by the approved SIP and will not delay those
reductions given that the limit is currently effective. We, therefore,
propose to find that approving CDPR's commitment to manage VOC
emissions from agricultural and commercial structural pesticide use to
ensure that they do not exceed 18.1 tpd in the SJV area into the
California SIP will not interfere with any requirement concerning
attainment and reasonable further progress or any other applicable
requirement of the CAA.
In comments that EPA received on its proposed approval of the SJV
2004 Extreme Ozone Attainment Plan (74 FR 33933(July 14, 2009)),
several non-governmental organizations argued that the 1994 Pesticide
Element requires a 20 percent reduction in VOC emissions from 1990
levels by 2005 in the SJV citing to the Boyd letter on page A-2.\27\
---------------------------------------------------------------------------
\27\ See letter, Brent Newell, Legal Director, Center on Race,
Poverty & the Environment, August 31, 2009, ``Comments on Approval
and Promulgation of Implementation Plans: 1-Hour Ozone Extreme Area
Plan for San Joaquin Valley, CA (Docket No. EPA-R09-OAR-2008-
0693),'' pp. 16-20.
---------------------------------------------------------------------------
In the Boyd letter, CARB provided EPA with suggested revisions to
our March 18, 1996 (61 FR 10920, 10935) proposed approval of the 1994
Ozone SIP. In reference to the 1994 Pesticide Element, CARB stated that
the ``commitment is for a 20% reduction from 1990 levels by 2005 in
each SIP area, except [San Diego]. [CARB] only took credit in the
attainment year: SJV 1999 = 12%; Sac 2005 = 20%; Ven 2005 = 20%; SED
2007 = 20%; SC 2010 = 20%.'' EPA does not find the ``commitment is for
a 20% reduction'' statement determinative as to the State's commitment
for SJV, not only because it is immediately contradicted by the
statement that a 12 percent credit was taken only in the attainment
year of 1999 but also because it is not entirely consistent with the
more extensive language describing the emissions reductions target in
other parts of the approved 1994 Pesticide Element and does not reflect
the reductions relied on in the SIP.
The 1994 Pesticide Element committed CDPR to a ``maximum of 20
percent'' reduction in pesticide VOC emissions from 1990 baseline
levels in areas ``which reference VOC reductions'' from the element in
their plans. See 1994 Pesticide SIP, p. 1. With this language, the
percent reduction required in an area is tied to the emissions
reductions referenced, that is, relied on, in that area's plan. As
approved, the 1994 Pesticide Element also allowed for reductions of
less than 20 percent if fewer VOC reductions from pesticide were
needed. Id. As noted above, the reductions relied on in the 1994 Ozone
SIP in its attainment demonstration for SJV in 1999 were 13 tpd (in
1994 SIP currency) which equates to 12 percent reduction from 1990
baseline in 1999 (when anticipated growth in pesticide VOC emissions
between 1990 and 1999 is excluded) and no additional reductions have
been relied on in any SIP for SJV subsequent to the 1994 one.
Approval of the revised ``Pesticide Emission Reduction Commitment
for the San Joaquin Valley'' (submitted in 2009) will not interfere
with any applicable requirement related to attainment or reasonable
further progress for any PM2.5 or PM10 standard
in the SJV. EPA has determined that VOC controls are not required for
particulate matter control in the SJV. See 72 FR 20586, 20589 (April
25, 2007), 69 FR 30006, 30007 (May 26, 2004), and 76 FR 69896, 69924
(November 9, 2011).
Additional information on EPA's determination under CAA section
110(l) can be found in section II.D. of the TSD for this proposal.
IV. Response To Remand in Association of Irritated Residents Case
In this section, we discuss why EPA believes that our proposed
approval of the fumigant regulations and commitment for the SJV obviate
the need to rescind or modify EPA's previous approvals of the
California SIP Pesticide Element notwithstanding the deficiencies in
the 1994 Pesticide Element that have been brought to light by
subsequent litigation. In so doing, we summarize the relevant
background that provides the context for this explanation.
In 1994, California submitted the 1994 Pesticide SIP as part of its
comprehensive 1994 Ozone SIP. The 1994 Pesticide SIP set forth the goal
of reducing VOC emissions from pesticide use by as much as 20 percent
from 1990 levels as needed in those areas of California that relied on
emissions reductions from pesticides to meet CAA requirements for
attainment of the 1-hour ozone standard. The 1994 Pesticide SIP
included a process for re-evaluation of pesticide products (to refine
emissions estimates and to review for possible restrictions on use),
for establishing the 1990 base year inventory and for tracking
emissions, for reducing VOC emissions from pesticide use through
voluntary changes in pest management practices, and for developing
additional regulatory measures to ensure that reductions are achieved.
Upon review of the 1994 Pesticide SIP, EPA identified certain
completeness and approvability issues and requested clarification. See
letters, David P. Howekamp, Director, Air and Toxics Division, EPA
Region 9 to James W. Wells, Director, CDPR, March 20, 1995 and April
21, 1995. CDPR responded to EPA's request with a clarification of the
1994 Pesticide SIP that established a commitment on the part of CDPR
``to adopt and submit to U.S. EPA by June 15, 1997, any regulations
necessary to reduce [VOC] emissions from agricultural and commercial
structural pesticides by specific percentages of the 1990 base year
emissions, by specific years, and in specific nonattainment areas,'' as
listed in a table showing percent reductions of 8, 12, 16, and 20
percent by 1996, 1999, 2002, and 2005, respectively, in the following
nonattainment areas: South Coast, Southeast Desert, Ventura, San
[[Page 24448]]
Joaquin Valley, and Sacramento Metro. See letter, James W. Wells,
Director, CDPR, to David P. Howekamp, EPA Region 9, March 31, 1995; the
Wells memorandum; and the related transmittal letter for the Wells
memorandum from James D. Boyd, Executive Officer, CARB to Felicia
Marcus, Regional Administrator, EPA Region 9, May 11, 1995.
In March 1996, EPA proposed to approve the 1994 Pesticide Element,
among other elements of the 1994 Ozone SIP and did so based in part on
the clarification provided by CDPR through the Wells memorandum. See 61
FR 10920, 10935-10936 (March 18, 1996). In response to EPA's proposed
rule, CARB submitted a letter stating: ``In the pesticide element of
the SIP, the [CDPR] projected a steady decline in volatile emissions
from pesticides between 1996 and 2005. However, California took SIP
credit for these reductions only in the applicable attainment year for
the San Joaquin Valley, Sacramento Region, Ventura County, the
Southeast Desert, and the South Coast. The notice should reflect this
information.'' See letter, James M. Strock, Secretary for Environmental
Protection, California Environmental Protection Agency, to Felicia
Marcus, Regional Administrator, EPA Region 9, May 2, 1996. CARB
subsequently submitted the Boyd Letter providing additional detail that
was intended to supplement the technical corrections identified in the
State's formal May 2 comment letter. Through the Boyd Letter, CARB
clarified again that CDPR's commitment was for a 20 percent reduction
from 1990 levels by 2005 in the five specified nonattainment area but
also noted that CARB only took credit in the attainment year, which
CARB specified as a 12 percent reduction by 1999 in San Joaquin Valley,
and 20 percent reduction in the attainment years for the four other
nonattainment areas.\28\
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\28\ At the time of EPA's action on the 1994 California Ozone
SIP and related 1994 Pesticide Element, the SJV was classified as a
``serious'' nonattainment area for the 1-hour ozone standard with an
applicable attainment date of 1999. See 61 FR 10920, 10925. Years
after approval of the 1994 SIP, the SJV was reclassified as
``severe'' and then ``extreme'' for the 1-hour ozone standard. See
66 FR 56476 (November 8, 2001) and 69 FR 20550 (April 16, 2004).The
other four areas were classified as ``severe'' or ``extreme'' with
later attainment dates at the time of EPA's action on the ozone SIP
and Pesticide Element.
---------------------------------------------------------------------------
In 1997, EPA took final action to approve the 1994 Pesticide
Element, and most of the 1994 California Ozone SIP and again referred
to the Wells memorandum as providing the clarification necessary to
provide EPA with the basis to approve the 1994 Pesticide Element as
meeting the applicable requirements for enforceability of SIP
revisions. See 62 FR 1150, 1169-1170 (January 8, 1997). However, in the
1997 final rule, EPA referred explicitly to California's request in its
May 2, 1996 comment letter to exclude emissions reductions for interim
years from the SIP, and also implicitly referred to the Boyd Letter by
citing CARB's decision not to assign credit to the pesticides measure
except for purposes of attainment. In the final rule, we tried to
reconcile the Wells memorandum with California's comment letter and the
Boyd letter and summarized what we believed the Pesticide Element to
contain with respect to regulatory measures, as follows: ``As described
in the SIP, California has committed to adopt and submit to U.S. EPA by
June 15, 1997, any regulations necessary to reduce VOC emissions from
agricultural and commercial structural pesticides by 20 percent of the
1990 base year emissions in the attainment years for Sacramento,
Ventura, Southeast Desert, and the South Coast, and by 12 percent in
1999 for the San Joaquin Valley.'' Id. at 1170.
In listing the specific portions of the 1994 Ozone SIP and related
documents that we were approving and incorporating as part of the
California SIP in our 1997 final action, we listed CDPR's 1994
Pesticide SIP and the Boyd Letter, but did not list the Wells
memorandum. While EPA's failure to approve and incorporate the Wells
memorandum into the SIP may have been inadvertent, California's May 2,
1996 comment letter and the Boyd Letter made such approval and
incorporation (i.e., without modification) problematic because the
Wells memorandum contained interim year emissions reduction commitments
that the California comment letter and Boyd Letter specifically
excluded.
In the mid-2000's, several community groups sued CDPR under the CAA
for failure to adopt and submit regulations ensuring VOC emissions
reductions from pesticide use in Ventura County based on the
commitments set forth in the Wells memorandum. Upon review of the
record, the Ninth Circuit Court of Appeals in effect denied the
community group the remedy that the group sought based on the court's
determination that the Wells memorandum was not in fact approved into
the California SIP and thus the commitment by CDPR to adopt and submit
regulations as set forth in the Wells memorandum was not enforceable
under the Act. See El Comit[eacute] para el Bienestar de Earlimart v.
Warmerdam, 539 F.3d 1062 (9th Cir. 2008) (Warmerdam). In the wake of
the Warmerdam decision, the community group filed a petition for review
in the Ninth Circuit challenging EPA's 1997 approval of the 1994 Ozone
SIP on the grounds that, without the Wells memorandum, EPA's approval
of that SIP was arbitrary and capricious because it relied on
unenforceable emissions reductions from the 1994 Pesticide Element. See
El Comit[eacute] para el Bienestar de Earlimart v. EPA, No. 08-74340
(``El Comit[eacute]''). The Ninth Circuit has not issued its decision
in the El Comit[eacute] case against EPA's approval of the 1994 Ozone
SIP.
Meanwhile, in 2004, California resubmitted the 1994 Pesticide
Element to EPA as part of the 2003 State Strategy, which was originally
intended to replace the state measures potion of the 1994 California
Ozone SIP in the California SIP, in the form of a control measure
referred to as ``PEST-1.'' PEST-1 was simply a continuation of the
original 1994 Pesticide Element. In 2009, we approved PEST-1 as part of
our approval of the 2003 State Strategy reasoning that approval or
disapproval of PEST-1 amounted to the same thing from the standpoint of
the California SIP, namely the 1994 Pesticide Element. See 74 FR 10176
(March 10, 2009). EPA's approval of PEST-1 was challenged and the Ninth
Circuit disagreed with EPA's decision that approval or disapproval of
PEST-1 amounted to the same thing and remanded the approval of PEST-1
back to EPA for an evaluation of the Pesticide Element for
enforceability. See Association of Irritated Residents v. EPA, 632 F.3d
584 (9th Cir. 2011), revised January 27, 2012 (AIR). Specifically, the
Ninth Circuit held, given its earlier finding in the Warmerdam case
that the Wells memorandum was not approved and incorporated into the
California SIP, that EPA must determine whether the approved 1994
Pesticide Element has sufficient enforcement mechanisms to satisfy the
requirements of the CAA. In light of the decision in AIR, EPA filed a
supplemental brief that argues that the decision in the AIR case makes
the El Comit[eacute] case moot on the grounds that the relief granted
in the AIR case with respect to PEST-1 amounts to the same relief that
the petitioner could gain by a favorable decision in the El
Comit[eacute] case, namely re-evaluation of the Pesticide Element for
enforceability. The petitioners in the El Comit[eacute] disagree that
the AIR decision has made the El Comit[eacute] case moot, and the Ninth
Circuit has not yet issued its decision in the El Comit[eacute] case.
[[Page 24449]]
In light of the remand in the AIR case and with due consideration
to the history summarized above, we must re-evaluate the enforceability
of the 1994 Pesticide Element recognizing that the Wells memorandum is
not approved into the SIP and take appropriate remedial actions if the
element (without the Wells memorandum) does not meet the minimum
requirements for enforceability under the CAA. We are using this
proposed rule on the submitted fumigant regulations and revised SIP
commitment for the SJV as the opportunity to present our re-evaluation
and to explain our rationale for taking no action to rescind or modify
our approvals of the 1994 Pesticide Element in 1997 and again (as PEST-
1) in 2009.
First, we recognize that the 1994 Pesticide Element is a
``committal'' measure rather than a ``control'' measure. That is, the
1994 Pesticide Element constitutes a measure for which the State does
not provide regulations (or equivalent enforceable mechanism) in
support of the emissions reductions credited to the measure at the time
EPA takes action on the RFP or attainment demonstration plan that
relies on the emissions reduction, but commits to adopt and submit
regulations in support of the emissions reductions prior to the time
when the reductions are needed for RFP or attainment. EPA has found,
under certain circumstances, that committal measures that are relied on
to meet RFP, attainment, and/or other emissions reductions requirements
of the CAA to be enforceable, and thus approvable, only if such
measures identify the responsible party, applicability, adoption dates
for rules (if applicable), implementation dates, and emissions
reductions in terms of emissions rates (such as tons per day) equal to
the credit taken in the RFP or attainment plan for the committal
measure.
Back in 1995, when EPA reviewed the 1994 Pesticide SIP, we sought
clarification from CDPR on whether the 1994 Pesticide SIP establishes a
commitment to limit VOC emissions from pesticides to specific
percentages of the 1990 base year emissions by specific years in
specific nonattainment areas, regardless of future growth in emissions
that might otherwise occur and whether the Pesticide Element
establishes a commitment to adopt any regulations by a specific month
prior to the implementation date. See letter, David P. Howekamp,
Director, Air and Toxics Division, EPA Region 9 to James W. Wells,
Director, CDPR, March 20, 1995. Later, we requested that CDPR modify
the SIP to be explicit as to the dates of rule adoption and submittal
and the emissions reductions by date and area. See letter, David P.
Howekamp, Director, Air and Toxics Division, EPA Region 9 to James W.
Wells, Director, CDPR, April 21, 1995. The clear implication in EPA's
request to CDPR is that EPA believed at the time that such a
modification of the 1994 Pesticide SIP was necessary to meet the
minimum level of enforceability for crediting the emissions reductions
from such a committal measure. CDPR's response, via CARB, was the Wells
memorandum.
EPA's views on acceptable committal measures have not changed
significantly since the time of EPA's review and approval of the 1994
Pesticide Element in 1997, and thus, we can infer from the
correspondence between EPA and CDPR cited above and EPA's statements in
both the 1996 proposed rule and 1997 final rule that, in the absence of
the Wells memorandum, EPA would not have approved the 1994 Pesticide
Element on the grounds that it does not meet the minimum level of
enforceability that the CAA requires. See, generally, CAA section
110(a)(2) (``Each such plan shall (A) include enforceable emission
limitations and other control measures, means, or techniques * * * as
may be necessary or appropriate to meet the applicable requirements of
[the CAA]''). We have no reason to conclude otherwise today, and thus,
we affirm that, absent a commitment providing the specificity found in
the Wells memorandum, the 1994 Pesticide Element does not meet the
minimum requirements for enforceability of SIP committal measures.
Second, we discuss what actions EPA should take to address the
deficiency in enforceability of the 1994 Pesticide Element as discussed
above. We do so recognizing that CDPR has, since EPA's approval of the
1994 Pesticide Element, adopted and (via CARB) submitted regulations
that in effect have converted many of the non-regulatory provisions in
the 1994 Pesticide Element into a regulatory form. Specifically, CDPR
has adopted and submitted regulations restricting the use of field
fumigant application methods; requiring CDPR to annually inventory and
report pesticide VOC emissions for each area; establishing pesticide
use recordkeeping and reporting requirements; and creating a
contingency field fumigation limit and allowance program for Ventura.
These are the types of regulations that the commitment in the Well
memorandum would have made enforceable had the Wells memorandum been
approved into the SIP, and thus, we find no need to perfect the
commitment to regulations in the 1994 Pesticide Element because the
actual submittal of the regulations themselves obviates the need for an
enforceable commitment to submit those same regulations.
While we believe that the submitted CDPR regulations fulfill the
otherwise unenforceable commitment in the 1994 Pesticide Element to
adopt and submit regulations, the question remains whether the
regulations alone suffice to ensure that the emission reduction targets
(20 percent from 1990 levels in the South Coast, Southeast Desert,
Ventura, and Sacramento Metro areas and 12 percent from 1990 levels in
San Joaquin Valley) are met. Based on our review of the regulations for
this proposed action, we find that compliance with the emission
reductions targets is provided through CDPR regulations limiting field
fumigant application to lower-emitting methods and establishing a
fumigant emissions limit and allocation system for Ventura County and
monitored and enforced through regulations that require recordkeeping
and reporting of pesticide usage and CDPR to annually evaluate and
report VOC emissions from pesticides in each area.
These provisions are adequate to ensure that the emission reduction
targets are met in the Sacramento Metro, South Coast, and Southeast
Desert areas given that VOC emissions from pesticide use are typically
60 percent lower than 1990 levels in Sacramento Metro and Southeast
Desert and 80 percent lower than 1990 levels in the South Coast. See
CDPR's Annual Report on Volatile Organic Compound Emissions from
Pesticides: Emissions for 1990-2010 (March 2012), page 3. To a large
degree, the reductions in VOC emissions from pesticide use (relative to
1990 levels) in these three areas have resulted from permanent changes
in land use, although CDPR's regulations still serve an important
function by reducing the VOC emissions from remaining pesticide use in
the areas and by establishing a regulatory mechanism to track VOC
emissions from this source category that could, if necessary, provide
the basis for additional regulatory measures if, for some reason, VOC
emissions from pesticide use were to increase significantly over
current levels.
For Ventura County, in recognition that VOC emissions from
pesticide use are predominantly from fumigant use and are high enough
that they could, in a given year due to fluctuations in pesticide use,
violate the 20 percent emission reduction target, CDPR has submitted,
and we are proposing to
[[Page 24450]]
approve, additional regulatory provisions for that area. These Ventura-
specific provisions require CDPR to set a field fumigant VOC emissions
limit in its annual VOC emissions inventory report if overall pesticide
emissions (not just fumigant emissions) in the Ventura nonattainment
area are found to be within five percent of or exceed the listed
benchmark. The benchmark is equivalent to the 20 percent emissions
reduction target called for in the 1994 Pesticide Element for the
Ventura area. The Ventura-specific provisions also require the county
agricultural commissioner to add conditions to field fumigation permits
or take other actions to prevent the field fumigation limit from being
exceeded. As such, the regulations reasonably ensure that the 20
percent emissions reduction target would be met in Ventura County.
For the San Joaquin Valley, CDPR's regulations restricting fumigant
application methods and establishing requirements on CDPR to inventory
and report VOC emissions from pesticide use apply just as they do in
the other four nonattainment areas. While these regulations and other
measures have decreased VOC emissions from pesticide use in the SJV
such that current VOC emissions are approximately 18 percent less than
1990 levels, CDPR concluded that a mechanism was needed to supplement
the regulations to ensure that the 12 percent emission reduction target
would be met in the SJV. The supplemental mechanism chosen by CDPR is
the adoption of a commitment, which we are proposing to approve in
today's action, to manage VOC emissions from commercial structural and
agricultural pesticide use, such that the related VOC emissions do not
exceed 18.1 tons per day in the SJV. This level of emissions reflects a
12 percent emissions reduction from 1990 level of VOC emissions from
pesticide use. The specific measures that CDPR would undertake to bring
emissions back down to that level in the event that the annual
inventory reveals that the 18.1 tons per day emissions level had been
exceeded are not specified.\29\ Considered in isolation, the revised
commitment for San Joaquin Valley changes the form of the commitment in
the 1994 Pesticide Element for the SJV but does not represent an
enforceable measure for SIP purposes. However, when viewed in light of
the CDPR's regulations, the combination of the commitment and fumigant
regulations does meet the minimum requirements for enforceability of
SIP measures and reasonably ensures that the 12 percent emissions
reduction target from the 1994 Pesticide Element would be achieved in
San Joaquin Valley.
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\29\ CDPR has presented options for these measures. See CDPR
presentation ``Volatile Organic Compound Emissions from Pesticides:
Options for Reducing Non-Fumigant Emissions'' September 2011 and
November 2011, which can be found at https://www.cdpr.ca.gov/docs/emon/vocs/vocproj/nonfum_options_091611.pdf https://www.cdpr.ca.gov/docs/emon/vocs/vocproj/nonfum_options_prec_111811.pdf.
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For the reasons stated above, we conclude that there is no need to
rescind or otherwise modify our 1997 approval of the 1994 Pesticide
Element or our 2009 approval of PEST-1 notwithstanding the deficiencies
in enforceability in the 1994 Pesticide Element due to the absence of
an enforceable mechanism like the Wells memorandum. In short, this is
because CDPR's regulations and revised commitment for the San Joaquin
Valley provide the enforceable mechanism that would otherwise be
lacking in the 1994 Pesticide Element. If EPA approves the regulations
and commitment, as proposed herein, then the 1994 Pesticide Element
would be fulfilled. If, after consideration of comments, EPA concludes
that the regulations and commitment do not meet the applicable CAA
requirements, then the decision regarding EPA's previous actions on the
1994 Pesticide Element would need to be reconsidered.
V. Proposed Actions and Opportunity for Public Comment
For the reasons discussed above, EPA is proposing to approve under
CAA section 110(k)(3) the revisions to the California SIP Pesticide
Element submitted by CARB on October 12, 2009 and August 2, 2011 and to
incorporate them into the California's federally-enforceable SIP. We
are deferring action on the set of regulations submitted by CARB August
2, 2011 related to incorporating requirements related to methyl iodide
into the fumigant regulations.
Based on the proposed approval of these SIP revisions, EPA does not
plan to rescind or modify the Agency's prior approvals of the Pesticide
Element because the Agency has concluded that the revisions fulfill the
commitments of the original Pesticide Element, thus obviating the need
to address the deficiencies in enforceability of those original
commitments.
We encourage the public to comment on these proposals. Comments
will be accepted for 30 days following publication of the proposal in
the Federal Register. The deadline and a list of options for submitting
comments is provided at the DATES and ADDRESSES sections at the
beginning of this preamble.
VI. Statutory and Executive Order Reviews
Under the CAA, 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, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely proposes to approve state law as meeting Federal
requirements and does not propose to 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 Order
12866 (58 FR 51735 (October 4, 1993));
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 CAA; and
Does not provide EPA with the discretionary authority to
address, as appropriate, disproportionate human health or environmental
effects, using practicable and legally permissible methods, under
Executive Order 12898 (59 FR 7629 (February 16, 1994)).
In addition, this proposed action does not have Tribal implications
as specified by Executive Order 13175 (65 FR 67249; November 9, 2000),
because the SIP is not approved to apply in Indian country located in
the State, and
[[Page 24451]]
EPA notes that it will not impose substantial direct costs on Tribal
governments or preempt Tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Intergovernmental
relations, Ozone, Reporting and recordkeeping requirements, Volatile
organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: April 13, 2012.
Jared Blumenfeld,
Regional Administrator, Region 9.
[FR Doc. 2012-9850 Filed 4-23-12; 8:45 am]
BILLING CODE 6560-50-P