Revisions to the California State Implementation Plan, Imperial County Air Pollution Control District, 39366-39390 [2010-16350]
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R09–OAR–2010–0120; FRL–9169–2]
Revisions to the California State
Implementation Plan, Imperial County
Air Pollution Control District
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Final rule.
EPA is finalizing a limited
approval and limited disapproval of
revisions to the Imperial County Air
Pollution Control District (ICAPCD or
the District) portion of the California
State Implementation Plan (SIP) under
the Clean Air Act as amended in 1990
(CAA or the Act). This action was
proposed in the Federal Register on
February 23, 2010 and concerns local
rules that regulate coarse particulate
SUMMARY:
matter (PM10) emissions from sources of
fugitive dust such as construction sites,
unpaved roads, and disturbed soils in
open and agricultural areas in Imperial
County.
DATES: Effective Date: This rule is
effective on August 9, 2010.
ADDRESSES: EPA has established docket
number EPA–R09–OAR–2010–0120 for
this action. The index to the docket is
available electronically at https://
www.regulations.gov and in hard copy
at EPA Region IX, 75 Hawthorne Street,
San Francisco, California. While all
documents in the docket are listed in
the index, some information may be
publicly available only at the hard copy
location (e.g., copyrighted material), and
some may not be publicly available in
either location (e.g., CBI). To inspect the
hard copy materials, please schedule an
appointment during normal business
hours with the contact listed in the FOR
FURTHER INFORMATION CONTACT section.
FOR FURTHER INFORMATION CONTACT:
Andrew Steckel, EPA Region IX, (415)
947–4115, Steckel.andrew@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we,’’ ‘‘us’’
and ‘‘our’’ refer to EPA.
Table of Contents
I. Summary of Proposed Action
II. Public Comments and EPA Responses
III. EPA Action
IV. Statutory and Executive Order Reviews
I. Summary of Proposed Action
On February 23, 2010 (75 FR 8008),
EPA proposed a limited approval and
limited disapproval of the following
rules listed in Table 1, known
collectively as Regulation VIII, that were
adopted by ICAPCD and submitted by
the California Air Resources Board
(ARB) for incorporation into the
California SIP for the Imperial County
serious PM10 nonattainment area.
TABLE 1
Local agency
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ICAPCD .......
Rule No.
800
801
802
803
804
805
806
Rule title
General Requirements for Control of Fine Particulate Matter .......................................
Construction & Earthmoving Activities ...........................................................................
Bulk Materials ................................................................................................................
Carry Out & Track Out ...................................................................................................
Open Areas ....................................................................................................................
Paved & Unpaved Roads ..............................................................................................
Conservation Management Practices ............................................................................
We proposed a limited approval
because we determined that these rules
improve the SIP and are largely
consistent with the relevant CAA
requirements. We simultaneously
proposed a limited disapproval because
some provisions of the rules conflict
with the CAA section 110(a)
requirement that SIP rules must be
enforceable and the requirement in
section 189(b)(1)(B) for implementation
of best available control measures
(BACM) in serious PM10 nonattainment
areas such as Imperial County. We
discuss these statutory requirements
and the Regulation VIII deficiencies in
detail in the proposed rule and in the
Technical Support Document for that
proposal (proposal TSD).1 In the
proposed rule and proposal TSD we also
discuss our determination of which
fugitive dust source categories
addressed by Regulation VIII are
significant and consequently require
BACM pursuant to EPA guidance. This
1 Our proposed rule and proposal TSD also
describe additional improvements that we
recommend for future ICAPCD modifications of the
rules. This final action is not based on those
recommendations. As a result, we do not respond
here to all comments we received on them.
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determination was based in part on our
2009 decision 2 to not concur with the
State’s request pursuant to EPA’s
exceptional events rule 3 (EER) to
exclude certain exceedances of the PM10
National Ambient Air Quality Standard
(NAAQS) in Imperial County from
consideration in regulatory actions
under the CAA.4
We summarize the Regulation VIII
deficiencies addressed in our proposed
rule below. These deficiencies concern
Regulation VIII provisions relating to
open areas, unpaved roads and
agricultural lands.
2 Letter with enclosure from Laura Yoshii (EPA),
to James Goldstene (ARB), Re: exceptional events
requests regarding exceedances of the PM10 NAAQS
in Imperial County, CA, December 22, 2009.
3 40 CFR 50.1(j) and 50.14.
4 Issues related to the Regulation VIII deficiencies,
significant source categories and our decision not
to concur with the State’s exceptional events
requests are addressed further below in our
responses to comments we received on the
proposed rule.
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Submitted
06/16/06
06/16/06
06/16/06
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06/16/06
A. BACM-Related Deficiencies for Open
Areas
1. Recreational Off-Highway Vehicle
Activity
While recreational off-highway
vehicle (OHV) 5 activity causes much of
the PM10 emissions from open areas in
Imperial County, Rule 804 regulates
only a small portion of these emissions,
including those from OHV activity on
State lands on which the rule is not
being implemented. The vast majority of
the OHV emissions in Imperial County
are addressed only by requirements in
Rule 800 section F.5 for dust control
plans (DCPs) for sources under the
control of the Bureau of Land
Management (BLM). While BLM is
required to describe in the DCPs the
dust control measures that it intends to
implement, BLM is not required to
implement any specific BACM-level
controls for OHV use. Moreover,
ICAPCD has not provided an analysis of
BACM for OHV activity, including
5 As used here and in the proposal TSD, the term
‘‘off-highway vehicle’’ or OHV includes all vehicles
subject to the exemption in Rule 800 section E.6 for
recreational use of public lands in Imperial County.
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potential OHV activity in open areas
and on unpaved roads and paths that
are exempt from the specific
requirements and measures in Rules 804
and 805. The proposed rule and
proposal TSD address how ICAPCD can
correct these deficiencies.6
2. Definition of ‘‘Disturbed Surface’’
The term ‘‘disturbed surface area’’ is
used in several Regulation VIII rules but
is never defined. For example, Rule 804
applies to a source category for which
BACM is required and relies on the
undefined term to describe rule
applicability in Rule 804 section B. A
definition of this term is necessary in
order to ensure that these rules are
enforceable at a BACM level.
B. BACM-Related Deficiencies for
Unpaved Roads
1. Unpaved Non-Farm Roads
While CAA section 189(b)(1)(B)
requires ICAPCD to implement BACM
by 2008 (i.e., four years after
reclassification to serious),7 Rule 805
section E.7 allows the County until 2015
to stabilize heavily-travelled unpaved
roads. This schedule is inconsistent
with the statutory requirement and
ICAPCD has not provided adequate
evidence that this schedule is as
expeditious as practicable, based upon
economic feasibility or any other
appropriate consideration. In addition,
Rule 805 section E.7’s requirement to
stabilize all non-exempt unpaved
County roads is not adequately
enforceable as currently structured
because it is not clear that the County
is required to implement (and not just
submit) a stabilization plan; stabilize
different unpaved roads each year; and
maintain all stabilized roads. The
proposed rule and proposal TSD
address how ICAPCD can correct these
deficiencies.8
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2. Unpaved Farm Roads and Traffic
Areas
Rule 805 section D.2 exempts
agricultural roads and traffic areas from
the opacity and stabilization
requirements applicable to nonagricultural operation sites. Farm roads
and traffic areas are only required to
implement a conservation management
practice (CMP) from the menus for
6 75 FR 8008, 8010–8011 and our proposal TSD,
section III.B.1.
7 On August 11, 2004, EPA reclassified Imperial
County as serious nonattainment for PM10. 69 FR
48835. Since 2008 has passed, BACM is now
required to be implemented as expeditiously as
practicable. Delaney v. EPA, 898 F.2d 687 (9th Cir.
1990).
8 75 FR 8008, 8011 and our proposal TSD, section
III.B.3.
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unpaved roads and traffic areas in Rule
806 in contrast to analogous rules in
other geographical areas.
Rule 806 sections E.3 and E.4 list
CMPs intended to control emissions
from agricultural unpaved roads and
traffic areas but these measures are
broadly defined and there is no other
mechanism in the rule to ensure
specificity. The absence of sufficiently
defined requirements makes it difficult
for regulated parties to understand and
comply with the requirements, and
makes it difficult for ICAPCD or others
to verify compliance and to enforce the
requirements if necessary. The lack of
specificity similarly renders it difficult
to assess whether the measures
constitute BACM level controls. The
proposed rule and proposal TSD
address how ICAPCD can correct these
deficiencies.9
3. Border Patrol Roads
Rule 800 section F.6.c exempts roads
owned or operated by the U.S. Border
Patrol (BP) from Rule 805 requirements
that are ‘‘inconsistent with BP authority
and/or mission.’’ It is not clear what this
exemption is intended to address, or
how it would be implemented and
enforced in order to meet BACM
requirements. The proposed rule
addresses how ICAPCD can correct
these deficiencies.10
C. BACM-Related Deficiencies for
Agricultural Lands
1. Tilling and Harvesting
Rule 806 sections E.1 and E.2 list
CMPs intended to control emissions
from agricultural land preparation and
cultivation (including tilling), and
harvest activities, but these measures
are broadly defined and there is no
other mechanism in the rule to ensure
specificity. The absence of sufficiently
defined requirements makes it difficult
for regulated parties to understand and
comply with the requirements, and
makes it difficult for ICAPCD or others
to verify compliance and to enforce the
requirements if necessary. The lack of
specificity similarly renders it difficult
to assess whether the measures
constitute BACM level controls.
In addition, Rule 806 section E
requires one CMP from the ‘‘land
preparation and cultivation’’ category
and one CMP from the ‘‘harvesting’’
category, while rules in other
geographic areas have more stringent
requirements.
9 75 FR 8008, 8011 and our proposal TSD, section
III.B.4.
10 75 FR 8008, 8011.
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The proposed rule and proposal TSD
address how ICAPCD can correct these
deficiencies.11
2. Windblown Dust
Windblown dust from non-pasture
agricultural lands is also a significant
source of PM10 that requires BACM
independent of agricultural tilling. The
CMPs in Rule 806 section E, however,
mainly control emissions by reducing
the number of vehicle passes across
fields, and sources are not required to
select BACM level practices for
controlling windblown dust from active
or fallow agricultural fields. The
proposed rule and proposal TSD
address how ICAPCD can correct these
deficiencies.12
D. Non-BACM Deficiency
Rule 802 section D.1 allows the Air
Pollution Control Officer (APCO) to set
aside controls that might be used
instead of water to stabilize surfaces of
bulk materials. This discretion allows
ICAPCD to approve alternatives to the
applicable SIP without following the
SIP revision process described in CAA
section 110. Moreover, ICAPCD has not
demonstrated why such discretion is
needed for measures such as covering,
enclosing or sheltering material piles.
The proposed rule addresses how
ICAPCD can correct these
deficiencies.13
II. Public Comments and EPA
Responses
EPA’s proposed action provided a 30day public comment period. During this
period, we received nine unique
comment letters from public agencies
and broad-based organizations.
• Brad Poiriez, Air Pollution Control
Officer, Imperial County Air Pollution
Control District, March 25, 2010
(ICAPCD).
• Daniel Steward, Acting Field
Manager, United States Department of
the Interior, Bureau of Land
Management, El Centro Resource Area,
March 24, 2010 (BLM).
• Kathleen Dolinar, District
Superintendent, Ocotillo Wells District,
California State Parks, Off-Highway
Motor Vehicle Recreation Division, by
e-mail dated March 24, 2010 (OWD).
• Gail Sevrens, Acting District
Superintendent, Colorado Desert
District, California State Parks, by e-mail
dated March 25, 2010 (CDD).
• David P. Hubbard, Gatzke Dillon &
Balance LLP, on behalf of EcoLogic
11 75 FR 8008, 8011–8012 and our proposal TSD,
section III.B.4.
12 75 FR 8008, 8012 and our proposal TSD,
section III.B.4.
13 75 FR 8008, 8012.
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Partners, Inc., March 25, 2010
(EcoLogic).
• Lisa T. Belenky, Senior Attorney,
Center for Biological Diversity, March
25, 2010, representing several listed
parties (CBD).
• Jose Luis Olmedo, Executive
Director, Comite Civico Del Valle, Inc.,
March 25, 2010, submitted and joined
by other parties (Comite).
• Ayron Moiola, Executive Director,
Coalition of Labor, Agriculture &
Business, March 24, 2010 (COLAB).
• Mark McBroom, President, Imperial
County Farm Bureau, March 24, 2010
(Farm Bureau).
We also received over 100 comment
letters from individuals and
organizations associated with
recreational OHV activities. We
reference these comments below by
their identification in the Federal docket
management system (FDMS) found at
regulations.gov. For example, the
comment listed in FDMS as document
number ‘‘EPA–R09–OAR–2010–0120–
0219’’ is referenced below as ‘‘0219.’’
We summarize the comments and
provide our responses below. In our
responses we identify specific
commenters in some cases but not in
others, particularly where many
commenters made similar points.
A. General
These overarching comments largely
provide general support or opposition to
our proposal.
General #1: CBD and Comite support
EPA’s proposal to find that the
Regulation VIII submittal does not fully
implement BACM level controls for all
significant source categories in Imperial
County, and support EPA’s
nonconcurrence with associated
exceptional event requests. They ask
EPA to finalize the proposed limited
disapproval of Regulation VIII and to
require additional PM10 emissions
restrictions. Many other commenters
disagree with EPA’s proposed limited
disapproval, especially with EPA’s
identification of deficiencies for BACM
requirements and EPA’s
nonconcurrence with exceptional
events. ICAPCD, for example, believes
that EPA’s proposal is arbitrary and
capricious, and that California has
demonstrated that all required BACM
are being implemented in Imperial
County.
Response: No response is necessary
for the overarching statements of
support or opposition. Responses are
provided below to the specific
comments that support these general
statements.
General #2: Several commenters
believe that EPA’s proposal lacks
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adequate scientific support. One (0144),
for example, states that passing
sweeping air quality regulations in an
area with unique terrain and climate
with only generalities to prove the
sources of pollution is unethical and
appears anti-development, anti-OHV
and anti-agriculture.
Response: The scientific support for
EPA’s action is documented in our
proposal and the associated proposal
TSD and discussed further in response
to specific comments below. See, for
example, response to comment EI #3
below. The serious health impacts of
exposure to elevated levels of PM10 are
well known and well documented and
need not be reiterated here.
General #3: ICAPCD objects to EPA
taking over four years to act on its
submittals of Regulation VIII for
approval and claims that EPA is only
now raising basic issues that ICAPCD
believes should have been resolved
before rule adoption. For example,
ICAPCD objects to EPA disapproving a
definition that it claims is clear and
understood by all affected parties.
ICAPCD and others (e.g., COLAB)
comment that EPA never raised this and
other concerns despite ICAPCD’s
extensive public process and
communication with EPA before rule
adoption. ICAPCD also cites EPA’s
testimony before the District Board in
which the Agency supported Regulation
VIII as BACM. As a result, ICAPCD
concludes that EPA’s proposal
undermines ICAPCD’s ability to rely on
EPA comments in the future.
Response: EPA reviews and
comments on many draft State and local
agency rules during their development
prior to submittal to EPA for formal
approval. It is generally more efficient
for all parties to identify and resolve
issues early in the process, rather than
after rules are adopted and submitted to
EPA for inclusion into the SIP. EPA’s
formal action on local rules, however,
can only occur through notice and
comment rulemaking after rules have
been officially submitted to EPA by the
State. If EPA determines during that
process that a submittal does not fulfill
relevant CAA requirements, we cannot
approve the submittal. Given time and
resource constraints, it is not always
possible for the Agency to identify or
analyze fully all issues before State or
local rule adoption. Moreover, EPA
must carefully consider all public
comments submitted on proposed EPA
actions on State and local rules. Such
comments often identify issues and
concerns that may not have arisen
during the prior evaluation of drafts of
a rule. We continue to believe, however,
that communication between EPA and
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State and local agencies at the rule
development stage is productive.
General #4: OWD asks EPA to extend
the comment period because it was
informed of EPA’s proposal only nine
days before the close of the comment
period. Several commenters also state
that EPA did not provide adequate
notification time (0218.1 and 0098) or
consultation with State Park personnel
(0218.1 and OWD).
Response: EPA denied OWD’s request
to extend the comment period because
EPA is under a court order 14 to finalize
action by June 15, 2010, and needs time
to analyze all comments submitted on
the proposal.15 While more time and
outreach before EPA action is always
desirable, nothing in the comments
suggests that EPA failed to follow
relevant public notification
requirements found in the
Administrative Procedures Act.16 EPA
notes that OWD did comment on the
proposal and EPA has taken those
comments into consideration in the
final action.
B. State Implementation Plan (SIP)
These comments generally address
broad SIP issues rather than specific
Regulation VIII provisions.
SIP #1: OWD believes the PM10
standard is nearly impossible to attain
given Imperial’s climate, natural desert
condition, the cost of inappropriate
BACM, and other local conditions. In
contrast, Comite asks EPA to find that
California has failed to submit a PM10
plan as required by 72 FR 70222
(December 11, 2007), and to consider
imposing associated CAA section 179
sanctions and a section 110(c) Federal
implementation plan (FIP) in this area.
Response: Our proposed action
addresses the CAA section 189(b)(1)(B)
requirement for BACM for certain PM10
sources in Imperial County. The
submittal at issue, Regulation VIII, is but
one portion of the complete SIP that
ICAPCD must develop in order to meet
additional CAA requirements. These
comments address the separate and
broader statutory obligations for the
State to submit a PM10 plan that, among
other things, demonstrates expeditious
attainment of the PM10 NAAQS. Those
other obligations are not the subject of
this action.
SIP #2: ICAPCD does not believe that
any additional controls such as those
that may need to be implemented if EPA
partially disapproves Regulation VIII
14 Comite Civico Del Valle, Inc., v. Jackson, No.
09–cv–04095 PJH (N.D. Cal.).
15 E-mail from Andrew Steckel, EPA, to Kathleen
Dolinar, California State Parks, March 29, 2010.
16 See 5 U.S.C. 553.
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will prevent PM10 exceedances during
high winds or otherwise materially
benefit air quality on days unaffected by
high winds. ICAPCD further believes
that such additional controls will waste
limited resources that should be used in
other ways to improve local air quality
in the area.
Response: CAA section 189(b)(1)(B)
and EPA guidance 17 require that BACM
be implemented for all significant
source categories 18 in serious PM10
nonattainment areas such as Imperial
County. As explained in our proposal,19
we determined that each of the
subcategories under open areas,
unpaved roads and agricultural lands
below meet or exceed the 5 μg/m3 de
minimis level in our guidance and are
therefore significant source categories in
Imperial County:
Open areas:
—Windblown Dust, Other Open Area.
Unpaved roads:
—Entrained Unpaved Road Dust, City/
County.
—Entrained Unpaved Road Dust, Canal.
—Windblown Dust, Unpaved City/
County Road.
—Windblown Dust, Unpaved Canal
Road.
—Windblown Dust, Unpaved Farm
Road.
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Agricultural lands:
—Tilling.
—Windblown Dust, Non-Pasture
Agricultural Lands.
As EPA stated in the guidance, the
structural scheme throughout title I of
the CAA, including its provisions for
the PM10 NAAQS, requires the
implementation of increasingly
stringent control measures in areas with
more serious pollution problems. EPA
further stated ‘‘that the more serious the
air quality problem, the more reasonable
it is to require States to implement
control measures of greater stringency
despite the greater burdens such
measures are likely to cause.’’ 20
Imperial County continues to violate the
PM10 standard 21 and our proposed
17 ‘‘State Implementation Plans for Serious PM–10
Nonattainment Areas, and Attainment Date Waivers
for PM–10 Nonattainment Areas Generally;
Addendum to the General Preamble for the
Implementation of Title I of the Clean Air Act
Amendments of 1990;’’ 59 FR 41998 (August 16,
1994) (General Preamble Addendum).
18 Under the General Preamble Addendum, a
source category ‘‘will be presumed to contribute
significantly to a violation of the 24-hour NAAQS
if its PM10 impact at the location of the expected
violation would exceed 5 μg/m3.’’ This is also
referred to as the de minimis level. Id. at 42011.
19 75 FR 8008, 8010, and proposal TSD, pp. 5–7.
20 General Preamble Addendum at 42010.
21 EPA’s Air Quality System Preliminary Design
Value Report (May 18, 2010) shows 17 exceedances
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action identifies several components of
the State’s Regulation VIII submittal
relating to open areas, agricultural lands
and unpaved roads that do not fulfill the
CAA BACM requirement and the
enforceability requirements of CAA
section 110(a).
We further address ICAPCD’s
contention that additional Regulation
VIII controls will not prevent PM10
exceedances during high winds in our
response to comment EE #1 below.
SIP #3: Many commenters emphasize
the importance of OHV areas in Imperial
County for recreation, and believe that
enjoyment of the desert should not be
restricted. Commenters note that many
organizations help keep the desert
clean, and one commenter (0175.1)
believes such efforts would be reduced
if OHV areas are closed.
Response: Recreation, enjoyment of
the desert and clean deserts are
certainly desirable, whether for OHV
use or otherwise. However, except as
implicit in our response to comment
OHV #5 below, they are not germane to
the evaluation in our proposal and in
this final rule of Regulation VIII and its
compliance with the applicable CAA
requirements.
SIP #4: Two commenters (OWD and
0218.1) question whether EPA’s
proposal is based on statistically
significant data since there were only
three PM10 exceedances within a three
year period.
Response: ICAPCD’s obligation to
implement BACM for Regulation VIII
fugitive dust sources derives from the
Imperial County’s designation as
nonattainment and classification as
serious. On November 15, 1990, the date
of enactment of the 1990 Clean Air Act
Amendments, Imperial County was
designated nonattainment and classified
as moderate.22 On August 11, 2004, EPA
reclassified the area as serious in
compliance with a mandate of the U.S.
Court of Appeals for the Ninth Circuit.23
The reclassification, pursuant to CAA
section 188(b)(2), was based on a
finding that the area failed to attain the
PM10 NAAQS by the statutory deadline
of December 31, 1994. Once reclassified
to serious, the area was required to
comply with CAA section 189(b)(1)(B),
which required that BACM be
implemented for the area four years
after its reclassification to serious.
The three exceedances to which OWD
refers occurred during 2006 and 2007.
of the 24-hour PM10 NAAQS in Imperial County
between 2007 and 2009.
22 56 FR 56694 (November 6, 1991).
23 69 FR 48792; Sierra Club v. United States
Environmental Protection Agency, et al., 346 F.3d
995 (9th Cir. 2003); cert. denied, 542 U.S. 919
(2004).
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The State requested that these
exceedances be excluded from use in
regulatory actions pursuant to EPA’s
EER.24 Because we did not concur with
the State’s request, BACM is required to
be implemented for certain windblown
dust source categories, including open
areas, for which such controls would
not have been required if we had agreed
with the State.25 See our responses to
Exceptional Events comments below.
We also note that California has
chosen to sample PM10 in Imperial
County only one out of every six days.
As a result, by regulation, each
monitored exceedance is estimated to
represent approximately six
exceedances rather than one.26 For
example, in 2009, ICAPCD reported
three monitored exceedances at the
Ethel Street monitoring site, which are
estimated to represent 18.3 exceedances.
Exceedances were also monitored at
Brawley, El Centro, Westmorland and
Niland in 2009.27
SIP #5: Comite believes PM10 should
be further controlled in Imperial County
by adoption of local fugitive dust
ordinances like those in Coachella’s
Cathedral City, and by strengthening
open burning regulations to be similar
to those in the South Coast Air Quality
Management District (SCAQMD) and
the San Joaquin Valley Unified Air
Pollution Control District (SJVUAPCD).
Response: We assume the commenter
refers to title 8, chapter 8.54 of
Cathedral City’s municipal code which
describes requirements for construction,
unpaved roads and other local dust
sources.28 These requirements are
generally similar to the type of controls
adopted by SCAQMD (e.g., Rule 403),
SJVUAPCD (e.g., Regulation VIII) and
ICAPCD (Regulation VIII). The
commenter does not identify any
specific Cathedral City controls that it
believes are needed in ICAPCD
Regulation VIII to constitute BACM.
Except where identified in our proposal,
we believe ICAPCD’s BACM analyses
include adequate evaluation of
analogous fugitive dust controls in other
areas.29 It is possible that the
commenter is recommending
duplicative city ordinances that overlap
County-wide Regulation VIII. While
such redundancy could improve
compliance, it is generally not necessary
24 See
section II.D.1 below.
FR 8008, 8010 and proposal TSD pp. 5–7.
26 40 CFR part 50, appendix K.
27 EPA’s Air Quality System Preliminary Design
Value Report (May 18, 2010).
28 Cathedral City Municipal Code, title 8, chapter
8.54, Fugitive Dust Control; https://qcode.us/codes/
cathedralcity/.
29 2009 PM
10 SIP table 4.2 and 2005 BACM
analysis table 4.2.
25 75
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to meet CAA section 110(a)
enforceability requirements.
Finally, our proposed action only
addresses the ICAPCD controls for
certain PM10 source categories
encompassed by Regulation VIII, and
therefore does not address control of
open burning or many other air
pollution sources in Imperial County.
See also responses to comments SIP #1
and EI #1.
SIP #6: Comite cites Vigil v. Leavitt,
381 F.3d 826, 834 (9th Cir. 2004) and
Hall v. EPA, 273 F.3d 1146 (9th Cir.
2001), in commenting that measures in
other areas can be considered BACM for
Imperial County and are per se feasible.
Comite further argues that what
constitutes BACM can strengthen over
time. In contrast, OWD does not believe
that Imperial County should apply
mitigation measures from other
geographic areas (e.g., SJVUAPCD and
Maricopa) that have different geologic
and other local conditions. Similarly,
COLAB believes that different cultural
practices prevent ICAPCD from blindly
implementing controls imposed in other
areas, although the ICAPCD and
SJVUAPCD CMP rules are very similar.
Still another commenter (0119) claims
that similar restrictions on construction,
OHVs, farmers, etc., in Las Vegas and
elsewhere have not been effective, and
there is no need for such draconian and
ineffective bureaucratic rules.
Response: EPA believes that it is
appropriate, when evaluating what
constitutes BACM for a given source
category, to consider controls that have
been adopted and implemented in other
geographical areas. EPA agrees that the
facts and circumstances in a given area
can affect what constitute BACM for
that area, but that this determination
must be based upon appropriate
consideration of relevant information
specific to that area.
Comite does not explain how the
cited cases support its position.
Nonetheless, we agree that in evaluating
BACM for Imperial County, ICAPCD
should analyze analogous measures in
other areas and that BACM may
strengthen over time.30 Our proposal
identifies several significant
deficiencies in ICAPCD’s analysis to
date.31 While BACM is determined on a
case-by-case basis 32 and, as such, the
analysis can include evaluation of local
conditions that might make specific
controls economically and/or
30 General
Preamble Addendum at 42013–42014.
OHV controls in Arizona Revised Statute
§ 49–457.03 and Clark County Air Quality
Regulations, section 90 (75 FR 8011, February 23,
2010).
32 General Preamble Addendum at 42010 and
42012.
31 E.g.,
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technologically feasible in one area but
not another,33 neither the 2009 PM10
SIP 34 nor the comment provides
sufficient detail to adequately address
the deficiencies identified in our
proposal.
OWD does not explain how Imperial
County differs so markedly from the San
Joaquin Valley and the Maricopa area
that it would be inappropriate to
consider BACM approved in those areas
as part of the evaluation of controls for
the same source categories in Imperial
County. Similarly, COLAB does not
elaborate on what ‘‘cultural practices’’ in
Imperial County would justify
disregarding approved BACM in the San
Joaquin Valley and the Maricopa area as
part of the evaluation of what controls
would be appropriate for comparable
source categories in Imperial County.
C. Emissions Inventory (EI)
EI #1: Many commenters oppose
further OHV controls because they
believe OHVs contribute little to
Imperial County’s PM10 pollution
problem compared to other sources.
Commenters identify various sources
they believe are more significant and/or
should be further addressed instead,
including fallow fields, fireplaces, feed
lots, agricultural burning, pesticides,
dirt roads, inefficient street lights,
insufficient public transportation,
insufficient speed limit enforcement,
Interstate 8, the New River, the Salton
Sea, Arizona to the east, San Diego to
the west, Mexican roads, fires and
factories to the south, rain, wind,
erosion, dust storms and other natural
occurrences. These commenters include
OWD, 0096, 0097, 0150, 0139, 0152,
0180, 0192, 0194 and 0219.1.
Response: Our proposal explains that
BACM is required for all significant
PM10 source categories in Imperial
County, that windblown dust from open
areas is a significant PM10 source
category, and that OHVs greatly increase
emissions from open areas in Imperial
County.35 Our proposal further explains
that ICAPCD has not demonstrated
implementation of BACM for open areas
with respect to OHVs.36 These
conclusions are based on inventory
information prepared by ICAPCD and
ARB and used during development of
33 In this respect, we do not agree with Comite
that measures adopted in other areas are
automatically transferable to Imperial County.
34 ‘‘2009 Imperial County State Implementation
Plan for Particulate Matter Less Than 10 Microns
in Aerodynamic Diameter, Final,’’ adopted by
ICAPCD Governing Board on August 11, 2009.
(2009 PM10 SIP).
35 Proposal TSD, pp. 5–8.
36 Id. at p. 8.
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Regulation VIII and the 2009 PM10
SIP.37
The inventory in the 2009 PM10 SIP
represents the most comprehensive
information currently available on OHV
emissions in Imperial County.38
ICAPCD’s analysis in the 2009 PM10 SIP
concluded that windblown dust from
open areas was not a significant source
category, but this conclusion was
premised upon many exceedences of the
NAAQS being deemed to be the result
of exceptional events. However, EPA’s
own conclusion regarding those
exceedences is that they were not
caused by exceptional events and, as a
result, we consider windblown dust
from open areas to be a significant
source category that is subject to the
CAA’s BACM requirement. See response
to comment SIP #4 and responses to
Exceptional Events comments in section
II.D below. Therefore ICAPCD has failed
to meet the BACM requirement for
windblown dust from open areas, in
part because ICAPCD has not evaluated
what controls might be appropriate for
OHV activities in such areas.
EPA’s action on the Regulation VIII
submittal does not address or depend on
whether additional controls may also be
appropriate for the various other sources
identified in the comments.
EI #2: One commenter (0188) had
driven past many farms in El Centro
during tilling and observes that the dust
was very minimal. Another (0201)
thinks more attention should be paid to
agriculture which the commenter
believes is exempt from many of the
environmental regulations.
Response: See response to comment
EI #1. Similar to emissions from open
areas, EPA has concluded that
emissions associated with tilling on and
windblown dust from agricultural lands
are significant source categories in
Imperial County and, as such, ICAPCD
needs to meet the BACM requirement
for such sources.39
The commenter (0201) concerned
about exemptions for agriculture did not
specify which regulations exempt
agriculture. As explained in our
proposal, however, because certain
agricultural-related activities constitute
a significant source category for PM10 in
Imperial County, ICAPCD is required to
meet the CAA’s BACM requirements for
such sources. Any ‘‘exemptions’’ for any
such sources would need to be justified
and explained in the context of meeting
the BACM requirements.
EI #3: Several commenters claim that
EPA has not proved the impact of OHVs
37 Id.
at pp. 5–8.
PM10 SIP, Chapter 3; Appendix III.
39 Proposal TSD, pp. 5–8 and 9–11.
38 2009
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on PM10 levels sufficient to require
additional OHV regulations. OWD
notes, for example, that: (1) EPA did not
analyze extreme terrain, thermal
stability and other effects on winds in
the desert; (2) most emissions from open
lands come from undisturbed shrub/
grassland which are not anthropogenic
sources; and (3) ICAPCD’s 2009 PM10
SIP, on which EPA relies, uses worstcase assumptions rather than actual soil
condition information to estimate that
OHVs represent less than 5% of the
County’s total PM10 emissions (13.9 of
282 tpd). OWD states that 99% of these
total emissions relate to OHVs subject to
Federal and State stewardship.
Therefore OWD concludes that actual
OHV emissions are small compared to
worst-case estimates. OWD also
questions EPA’s reference for the
estimate of 22 tpd of windblown PM10
from OHVs.
EcoLogic believes that EPA needs
monitoring in the Ocotillo Wells State
Vehicle Recreation Area (SVRA) and
other areas to show how specific OHV
activity affects sensitive receptors and
for EPA to identify OHV activity as a
major contributor to the County’s PM10
problem. Another commenter believes
EPA lacks data tying PM to specific
OHV activities (0218.1), and several
commenters believe that any pollution
from OHVs is virtually immeasurable.
Several commenters believe additional
inventory analysis is particularly
important because OHV areas are far
from population centers and monitors
with PM10 exceedances. One commenter
(0131) requests an unbiased third-party
study of OHV impacts. CDD explains
that PM10 emissions from several
specific parks in Imperial County
should be low, partly because OHV
activity is prohibited. In contrast, CBD
supports EPA’s claim that OHVs on
BLM land cause considerable PM10 in
Imperial County, and notes that BLM
previously estimated PM10 impacts from
OHV activities at the Aldodones Dunes
alone as high as 11 tpd on holiday
weekends.
Response: It is extremely difficult to
quantify and speciate accurately the
myriad sources of PM10 emissions and
PM10 precursor emissions spatially and
temporally for purposes of modeling air
pollution impacts and developing cost
effective control programs. As a result,
emission inventories are constantly
being refined as more and better science
and data become available. However,
EPA, State and local air pollution
agencies must make policy and
regulatory decisions based on the best
information available to comply with
the CAA. As discussed in response to
comment EI #1, the inventory and other
information underlying our proposal
regarding the emissions from OHV
activity and the impacts of such activity
represent the most comprehensive
information currently available.
Regarding specific concerns in this
comment:
(1) EPA’s conclusion that BACM is
required for OHV activity relies on
emissions inventory estimates that
ICAPCD developed. If appropriate,
ICAPCD could choose to refine those
estimates to take into consideration
factors such as terrain, thermal stability
and other effects on winds in the desert,
as well as distances between OHV areas
and population centers and additional
third party analysis. Such refinements
are beyond the level of detail normally
used in inventories required by CAA
section 172(c)(3).40
(2) ICAPCD in its 2009 PM10 SIP
quantifies the impact of soil type and
land cover (e.g., shrub/grassland) and
degree of OHV disturbance in OHV
emission estimates relied on by our
proposal.41
(3) ICAPCD used the best available
information regarding soil types in open
areas and determined that the remaining
uncertainty does not affect the results of
the technical analyses.42
(4) Even OWD’s 13.9 tpd OHV
emission estimate, which we believe is
too low,43 exceeds the presumptive 5
μg/m3 de minimis level for source
categories requiring BACM.44
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(5) The reference for 22 tpd of
windblown OHV emissions is
accurately explained in our proposal.45
The comment that monitoring is
necessary in the Ocotillo Wells SVRA
and other areas before EPA should
require controls for OHV activities is
incorrect. As stated previously, under
CAA section 189(b) and EPA guidance,
BACM is required for all significant
source categories in the nonattainment
area, including windblown dust in open
areas caused by OHV activity.46 Thus
monitoring, which could provide
valuable information, is nevertheless
not necessary to determine which
source categories require BACM.
D. Exceptional Events (EE)
1. Background
On March 22, 2007, EPA adopted a
final rule to govern the review and
handling of certain air quality
monitoring data for which the normal
planning and regulatory processes are
not appropriate.47 Under the rule, EPA
may exclude data from use in
determinations of NAAQS exceedances
and violations if a State demonstrates
that an ‘‘exceptional event’’ caused the
exceedances. Before EPA can exclude
data from these regulatory
determinations, the State must flag the
data in EPA’s Air Quality System
database and, after notice and
opportunity for public comment, submit
a demonstration to EPA to justify the
exclusion. After considering the weight
of evidence provided in the
demonstration, EPA decides whether or
not to concur with each flag.
On May 21, 2009, ARB submitted
demonstrations for ‘‘high wind’’ events
that allegedly caused ten exceedances of
the 24-hour PM10 standard at various
monitors in Imperial County in 2006
and 2007. The demonstrations consisted
of the following support documents
(listed in Table 2) prepared by ARB,
ICAPCD, and ICAPCD’s contractor,
ENVIRON:
TABLE 2
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Description
Document date
Natural Event Documentation: Calexico and Westmorland, California—September 2,
2006.
Natural Event Documentation: Brawley and Westmorland, California—April 12, 2007
[enclosed with June 13, 2008 letter to Sean Hogan].
January 30, 2009 ...................
September NED.48
April 15, 2008 .........................
Original April NED.
40 See, e.g., AP–42, Fifth Edition, Volume I,
Chapter 13: Miscellaneous Sources, 13.2.2—
Unpaved Roads, Final Section, EPA, November
2006. This document provides EPA guidance on
estimating emissions on unpaved roads and does
not, for example, account for road terrain. https://
www.epa.gov/ttn/chief/ap42/ch13/.
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PM10 SIP, appendix III.B.
PM10 SIP, p. 3–2.
43 In comparison to ICAPCD’s 22 tpd estimate.
Proposal TSD, footnote 32.
44 As discussed on pp. 5–8 of the proposal TSD,
depending on the specific monitor, 2–3% of
Imperial County’s annual inventory is calculated to
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42 2009
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result in a 5 μg/m3 contribution, which equates to
about 6–8 tpd emissions.
45 Id.
46 See, e.g., proposal TSD, p. 5.
47 ‘‘Treatment of Data Influenced by Exceptional
Events,’’ 72 FR 13560 (March 22, 2007) (EER).
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TABLE 2—Continued
Description
Document date
Natural Event Documentation: Brawley, Calexico, El Centro, Niland, and Westmorland,
California—June 5, 2007, Imperial County Air Pollution Control District [enclosed with
June 13, 2008 letter to Sean Hogan].
Natural Event Documentation: Brawley and Westmorland, California—April 12, 2007
[addendum to June 13, 2008 submittal].
Natural Event Documentation: Imperial County, California—June 5, 2007 [addendum to
June 13, 2008 submittal].
April 15, 2008 .........................
Original June NED.
March 12, 2009 ......................
April NED.
March 12, 2009 ......................
June NED.
As stated above in section I, on
December 22, 2009, EPA denied ARB’s
request to exclude all of the
exceedances as exceptional events. The
basis for our decision is specified in an
enclosure which accompanied the
December 22, 2009 letter.49 By letter,
including Attachment A and Appendix
A1, dated March 3, 2010, ICAPCD asked
EPA to reconsider this decision.50
Our proposal on Regulation VIII
explained that our 2009 EE decision led
to an adjustment of ICAPCD’s
significant source analysis which in
turn led us to modify the list of
significant sources for which BACM
must be implemented in Imperial
County under CAA section
189(b)(1)(B).51 As a result, our 2009 EE
decision was the subject of public
comments on our proposed action.
ICAPCD resubmitted its March 3, 2010
letter, including Attachment A and
Appendix A1, regarding our 2009 EE
decision as Appendix C to its March 25,
2010 comment letter on our Regulation
VIII proposed action.52 EPA also
received comments pertaining to our
exceptional events decision from
Comite and CBD. A summary of these
comments and our responses follow.
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2. Events Not Reasonably Controllable
or Preventable
EE #1: ICAPCD (Attachment)
disagrees with EPA’s interpretation of
the requirement in the EER at 40 CFR
50.1(j) that in order for an event to meet
the regulatory definition of exceptional
event, such event must be ‘‘not
reasonably controllable or preventable.’’
Specifically ICAPCD takes issue with
EPA’s statement in our 2009 EE decision
48 We refer to the natural event documentation in
these five documents, collectively, as the NEDs.
49 See footnote 2. We refer to our December 22,
2009 letter and the enclosure hereafter as ‘‘2009 EE
decision.’’
50 Letter from Brad Poiriez (ICAPCD) to Jared
Blumenfeld (EPA), March 3, 2010 with Attachment
A and Appendix A1.
51 See 75 FR 8010 and the proposal TSD, pp.
5–7.
52 We refer to ICAPCD’s March 10, 2010 letter
with its Attachment A and Appendix A1,
collectively, throughout our responses to the
exceptional events comments in section II.D as
‘‘Attachment.’’
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Abbreviated title
that this criterion inherently implies ‘‘a
requirement that the State demonstrate
that anthropogenic sources contributing
to the exceedance caused by the event
were reasonably well controlled.’’
ICAPCD believes that under the plain
regulatory language it is irrelevant
whether ‘‘reasonable and appropriate’’
controls are in place on the day of an
otherwise qualifying event when it can
be shown that such controls would not
reduce emissions and impact at the
monitor sufficiently to prevent the
exceedance. ICAPCD believes that it is
inconsistent with the intent of the CAA
for EPA to refuse to concur with an
exceptional event claim solely due to
EPA’s dissatisfaction with the
stringency of certain controls when such
controls could not have prevented the
exceedance.
Response: ICAPCD mischaracterizes
both the plain language and the
regulatory intent of 40 CFR 50.1(j) by
reading the words ‘‘reasonably
controllable or’’ out of that section. The
regulation clearly requires a showing
that the event is not either reasonably
controllable or preventable, not as
ICAPCD would have it, that the event
cannot be controlled to the extent that
no exceedance would have occurred.
Furthermore, ‘‘control’’ as generally used
in the CAA and EPA guidance (e.g.,
RACT and BACM 53), and as defined in
the dictionary means to regulate or to
reduce the incidence or severity.54 Thus
the meaning of the word ‘‘control’’
undeniably differs from the words
‘‘eliminate’’ or ‘‘prevent.’’ Therefore, to
meet the ‘‘not reasonably controllable or
preventable’’ criterion in 40 CFR 50.1(j),
states must demonstrate that reasonable
controls were implemented to regulate
or reduce emissions regardless of
whether the controls would have
prevented exceedances.55 Finally we
note that the relevance of dust controls
is inherent in the District’s own
characterization of the ‘‘event’’ as the
combination of wind and dust
entrainment from anthropogenic and
nonanthropogenic sources.56
As discussed in our 2009 EE decision,
the State failed to demonstrate that
reasonable controls were implemented
for anthropogenic sources contributing
to the exceedances, including
recreational OHVs and fallow
agricultural fields.57 Nor does ARB or
ICAPCD provide convincing evidence in
the NEDs or elsewhere to support the
claim that controls on these sources
could not have either prevented the
exceedances or reduced emissions.
EE #2: ICAPCD (Attachment) further
argues that the consequence of EPA’s
action would be to require control
measures beyond the area’s practical
abilities—a result the EER is specifically
designed to avoid. ICAPCD claims that
other specific provisions are in place to
prevent such difficulties, and ICAPCD
quotes from EPA guidance: ‘‘If emissions
from anthropogenic sources are reduced
to the point that it is no longer
technologically or economically feasible
to reduce those emissions further, and
the area still cannot attain the NAAQS,
the EPA may consider waiving the
serious area attainment date and
appropriate serious area
requirements.’’ 58
Response: The provisions to which
ICAPCD refers are contained in CAA
section 188(f) which authorizes EPA to
waive subpart 4 requirements applicable
to serious PM10 nonattainment areas,
including BACM, where EPA
determines that anthropogenic sources
of PM10 do not contribute significantly
to the violation of the standard in the
area. Under section 188(f), EPA may
53 ‘‘BACM is the maximum degree of emissions
reduction of PM10 and PM–10 precursors from a
source * * * which is determined on a case-by-case
basis, taking into account energy, environmental,
and economic impacts and other costs, to be
achievable for such source through application of
production processes and available methods,
systems, and techniques for control of each such
pollutant.’’ General Preamble Addendum at 42010.
54 Merriam-Webster’s Ninth New Collegiate
Dictionary.
55 Similarly, EPA explained in the preamble to
the EER that analysis of exceptional events includes
consideration of whether anthropogenic activities
have been controlled to the extent possible through
use of all reasonably available reasonable and
appropriate measures. 72 FR 13560, 13566, footnote
11.
56 E.g., September NED, p. 9.
57 2009 EE decision, section 4.2.
58 General Preamble Addendum at 42008.
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also waive a specific date for attainment
of the PM10 standard if the
Administrator determines that
nonanthropogenic sources contribute
significantly to a violation of the
standard.
In guidance, EPA has established the
same test for determining what
constitutes a significant contribution for
section 188(f) as is used for determining
the sources for which BACM must be
implemented under CAA section
189(b)(1)(B).59 The passage in the
guidance, quoted in isolation by
ICAPCD, is preceded by a lengthy
discussion regarding the circumstances
under which a serious area such as
Imperial County could qualify for
section 188(f) waivers. That discussion
makes clear that before EPA will
consider waiving a serious area
attainment date and requirements for a
serious area that failed to attain the
standard by the serious area deadline,
the State must demonstrate that BACMs
for significant anthropogenic sources
have been implemented and that the
area cannot attain the NAAQS with the
implementation of additional control
measures to achieve at least 5% annual
emission reductions pursuant to CAA
section 189(d). As discussed above and
in the proposal,60 ICAPCD has not
shown that BACM has been
implemented as required by CAA
section 189(b)(1)(B) for all significant
source categories in Imperial County.61
Thus it would be difficult to show that
additional controls are ‘‘beyond the
area’s practical abilities’’ or ‘‘no longer
technologically or economically
feasible’’ without a more thorough
BACM analysis.
EE #3: ICAPCD (Attachment) believes,
citing the preamble to the EER, that the
rule only requires reasonable controls
for anthropogenic sources within the
State.
Response: While Imperial County air
quality may be affected by emission
sources from areas outside California,
such as Arizona and Mexico, our 2009
EE decision relies on the lack of
demonstrated controls for
59 Id.
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60 75
at 42004.
FR 8008, 8010–8012 and proposal TSD, pp.
7–11.
61 The 2009 PM
10 SIP for Imperial County that is
intended to address the 5% requirement in CAA
section 189(d) was adopted by ICAPCD in August
2009 but has not been submitted to EPA by ARB.
The plan concludes that the area would have
attained the PM10 standard by the end of 2008 but
for transported emissions from Mexico and with the
‘‘exclusion of PM10 measurements affected by highwind exceptional events.’’ As a result of the claimed
exceptional events, with which we did not concur
in our 2009 EE decision, the plan also concludes
that ‘‘[t]he 5% yearly emission reductions
requirement does not apply to future years.’’ 2009
PM10 SIP, section 5.3.
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anthropogenic sources within
California.
EE #4: ICAPCD (Attachment) believes
that EPA has not specified criteria for
defining de minimis anthropogenic
sources in the EER context, explained
how the EER justifies such criteria, or
described feasible analyses to
implement such criteria.
Response: As noted above, our 2009
EE decision stated that inherent in the
‘‘not reasonably controllable or
preventable’’ criterion of the definition
of ‘‘exceptional event’’ in 40 CFR 50.1(j)
‘‘is a requirement that the State
demonstrate that anthropogenic sources
contributing to the exceedance caused
by the event were reasonably
controlled.’’ We also suggested that this
requirement be limited to ‘‘all non-de
minimis anthropogenic sources.’’ 62 In
this case, however, rather than further
interpreting the EER, we relied on
statements in the NEDs acknowledging
anthropogenic contributions in order to
determine which anthropogenic sources
were contributing to the 2006 and 2007
exceedances.63
EE #5: ICAPCD (Attachment) opposes
the statement in EPA’s 2009 EE decision
that ‘‘because implementation of BACM
is required in serious PM10 areas such
as Imperial County under section 189(b)
of the CAA, it is appropriate to consider
that level of control in evaluating
whether reasonable controls are in place
for purposes of the Exceptional Events
Rule.’’ Specifically, ICAPCD argues that
(1) such a standard would create a new
standard for exceptional event showings
that is inconsistent with the language
and intent of the EER which entails only
‘‘reasonable’’ and not ‘‘best’’ control of
anthropogenic sources; (2) the purpose
of the EER is to protect states from
consequences of reclassification as a
result of exceptional events; (3) by
definition, exceptional events fall
outside the normal planning process
and their analysis should not depend on
elements of the normal planning process
including designation status; and (4) the
meaning of ‘‘reasonable controls’’ for the
EER should not vary by an area’s
nonattainment status and should not be
as stringent as BACM.
Response: As stated in our 2009 EE
decision and in the preamble to the
EER, EPA addresses the EER criteria,
including that the event must be ‘‘not
reasonably controllable or preventable,’’
on a case-by-case basis considering the
weight of available evidence.64 Thus it
is appropriate to consider the totality of
EE decision, section 4.2.
id., section 4.2.1.
64 2009 EE decision, pp. 4 and 7; 72 FR 13560,
13569.
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63 See
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39373
circumstances in Imperial County in
determining what constitutes
‘‘reasonable’’ controls. We note again
that the County has been designated
nonattainment and classified as
moderate or serious since 1990. The
area was reclassified to serious in 2004.
In evaluating rules as RACM or
BACM, EPA has long considered it
appropriate to consider local conditions
since what is technologically and
economically feasible in one area may
not be in another.65 Moreover, EPA’s
2009 EE decision did not define
reasonable control as BACM in all cases
or suggest that the EER mandates such
an outcome. Rather, we stated that
‘‘[b]ecause implementation of BACM is
required in serious PM10 nonattainment
areas such as Imperial County under
CAA section 189(b), it is appropriate to
consider that level of control in
evaluating whether reasonable controls
are in place for purposes of the
Exceptional Events Rule.’’ 66 67 While
ICAPCD states that this is inappropriate
reliance on the normal planning
process, an area’s nonattainment
designation and classification are
inherently part of the local conditions
that are appropriately factored into what
controls are reasonable for purposes of
the EER. We also noted that ARB had
failed to demonstrate any meaningful
analysis of BACM or any other level of
control for either OHVs or fallow fields,
despite apparent significant emissions
and available controls imposed
elsewhere.68
EE #6: ICAPCD (Attachment)
comments that OHV emissions were
quantified in the 2009 PM10 SIP at
EPA’s request, but EPA ignored this
information in its analysis of the
exceptional event requests.
Response: It is the responsibility of
the State to submit demonstrations
addressing the EER criteria 69 to support
its exceptional event requests and it is
generally not appropriate or feasible for
65 See 57 FR 13498, 13540–13541 (April 16, 1992)
and the General Preamble Addendum at 42010.
66 2009 EE decision, section 4.2.2; 72 FR 70222.
67 We note that in EPA’s Natural Events Policy
which applied prior to the EER, we stated that
‘‘BACM must be implemented at contributing
anthropogenic sources of dust in order for PM–10
NAAQS exceedances to be treated as due to
uncontrollable natural events under this policy.’’
This requirement applied to moderate areas which
otherwise would not have been required to
implement BACM at all as well as to serious areas.
Thus, while the EER does not include such a
mandate, it is entirely appropriate and consistent
with the Agency’s past practice to consider a BACM
level of control in assessing whether reasonable
controls are in place. Memorandum from Mary D.
Nichols, EPA, ‘‘Areas Affected by PM–10 Natural
Events,’’ May 30, 1996, p. 5.
68 2009 EE decision, pp. 9–10.
69 40 CFR 50.14(c)(3).
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us to correct NED deficiencies by
searching for additional information.
Nonetheless, we did review the 2009
PM10 SIP before preparing the 2009 EE
decision and did not ignore ICAPCD’s
efforts to quantify OHV emissions in the
2009 PM10 SIP. In fact, the 2009 EE
decision references these efforts which
undermine the assumption in the
NEDs 70 that windblown dust from
desert areas is entirely from nonanthropogenic sources.71
EE #7: ICAPCD (Attachment) believes
it is not clear whether OHV sources
should be considered de minimis, what
controls EPA expects for illegal OHV
use, and why current regulations do not
constitute reasonable controls.
Response: As stated previously, the
State must demonstrate implementation
of reasonable controls in documentation
supporting exceptional events requests.
It is possible that ICAPCD/ARB may be
able to demonstrate in support of future
exceptional events requests that OHV
sources are de minimis, that there are no
reasonable controls for OHVs under
certain circumstances (e.g., certain
illegal uses), and/or that existing
regulations constitute reasonable
controls. The 2009 EE decision,
however, explains that the NEDs did not
provide meaningful analysis of any level
of control for OHVs, and that such
analysis should include as a starting
point evaluation of EPA’s RACM
guidance 72 and regulations adopted
elsewhere under similar conditions.73
EE #8: ICAPCD (Attachment)
comments that sand dunes are naturally
fully disturbed and that the 2009 PM10
SIP conservatively projects that OHVs
contribute only 0.9 tpd (10%) to the
total windblown emissions from them.
Other commenters similarly question
EPA’s assumption that OHVs disturb
desert crust. OWD, for example, notes
that dune laminae are often mistaken for
a crust but are broken by wildlife, foot
traffic and high winds.
Response: We agree that effective
control of fugitive dust is more difficult
for the sand dunes than for other parts
of Imperial County with different soil
types. As a result, the State may be able
to demonstrate in support of future
exceptional events requests, or for other
CAA purposes such as section
189(b)(1)(B) BACM, that dust control for
dunes should be different from and/or
less stringent than controls required for
other areas with different soil types.
However, the September NED failed to
provide meaningful analysis of
70 E.g.,
June NED, p. 2.
71 E.g., 2009 EE decision, footnotes 12, 15 and 16.
72 57 FR 18070, 18072 (April 28, 1992).
73 2009 EE decision, pp. 8–9.
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reasonable OHV controls for the sand
dunes or any other areas. This comment
has no bearing on the April and June
NEDs because the sand dunes were not
implicated by those events.
EE #9: ICAPCD (Attachment)
comments that OHV activity and related
direct PM10 entrainment should have
been negligible because of the high
winds during the April 12 and June 5,
2007 events and thunderstorms on
September 2, 2006. OWD notes that two
of the exceedance events occurred
during the OHV off-season and the third
occurred in April, when OHV use is also
low. Similarly, BLM comments that
OHV use is lowest when dust potential
is highest (June through September).
Response: Our 2009 EE decision
appropriately relies on OHV emission
information from the NEDs and the 2009
PM10 SIP which estimate large
windblown dust emissions and
significantly smaller directly entrained
emissions.74 Thus, even if no OHVs
operate and entrain dust on any
exceedance days, previous 75 OHV
activity still contributes to PM10
emissions by disturbing surfaces that
subsequently emit windblown dust. As
a result, documentation supporting
future Imperial County exceptional
events requests for events with
significant emissions from OHV areas
should include analysis of reasonable
controls for OHVs even if there is no
OHV activity during the exceedances.
EE #10: ICAPCD (Attachment)
comments that Regulation VIII
agricultural controls are well beyond the
reasonableness level required in the
EER. ICAPCD further states that it and
ARB have discussed agricultural
controls with EPA for many years,
worked with EPA during development
of the 2005 BACM analysis, closely
modeled Rule 806 on SJVUAPCD Rule
4550 which EPA approved in 2004, and
received EPA testimony in 2005 that
Regulation VIII, including Rule 806,
fulfilled BACM. ICAPCD also points out
that the emission inventory in the plan
shows that agricultural lands are
significantly less emissive than most of
the non-populated areas in Imperial
County.
Response: Our 2009 EE decision
explains that neither Regulation VIII nor
any other programs require any level of
emissions control of certain fallow
fields in Imperial County.76 Though
ICAPCD comments that emissions from
agricultural fields are smaller than
74 E.g., 22 tpd windblown and 1.34 tpd entrained
emissions, 2009 EE decision, p. 9.
75 Particularly recent activity where there has not
been time or conditions to repair surface crusts.
76 2009 EE decision, section 4.2.3.
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emissions from other sources in the
County, the NEDs for the exceptional
events requests do not identify any
anthropogenic sources as being de
minimis. Rather, there are summary
explanations that anthropogenic sources
are reasonably controlled through
Regulation VIII and other local
programs.77 The only anthropogenic
source discussed in any detail is
agriculture in the April and June NEDs.
These NEDs rely on the Imperial
Irrigation District’s (IID) fallowing
program as the basis for claiming that
reasonable measures were in place for
fallow fields which are not subject to
ICAPCD’s Conservation Management
Practices (CMP) Rule 806.78 However,
there were approximately 32,000 fallow
acres in Imperial County in 2007 that
were not subject to either Rule 806 or
IID’s program which is more than the
approximately 18,000 acres that were a
part of IID’s program in 2007.79 As
explained in our response to comment
EE #5, we stated in our 2009 EE
decision that it is appropriate to
consider a BACM level of control in
evaluating whether reasonable controls
are in place for purposes of the EER in
Imperial County. However, EPA found
no meaningful analysis of BACM or any
other level of control for fallow land
outside of IID’s program referenced or
provided in the NEDs.
EE #11: ICAPCD (Attachment)
comments that EPA’s 2009 EE decision
fails to mention Rule 806 in the
discussion of controls for agricultural
lands. ICAPCD notes that fallowed land
issues were included in the 2005 BACM
analysis 80 and concludes that failure to
address Rule 806 makes EPA’s
conclusions regarding agricultural areas
suspect.
Response: EPA did consider and
reference Rule 806 in our 2009 EE
decision.81 Although the 2005 BACM
analysis includes incidental references
to fallow lands, neither it nor the NEDs
attempts to quantify the fallow acreage
in Imperial County. Nor has the State
demonstrated how any existing
windblown dust controls might
constitute BACM for fallow fields
outside of IID’s program.
3. High/Unusual Wind Events
EE #12: Comite agrees with EPA’s
disapproval of ARB’s request to exclude
the monitored exceedances as
77 April and June NEDs, pp. 13–14, and
September NED, p. 18.
78 April and June NEDs, p. 13.
79 2009 EE decision, p. 9.
80 ‘‘Draft Final Technical memorandum:
Regulation VIII BACM Analysis,’’ October 2005
(2005 BACM Analysis).
81 2009 EE decision, p. 9.
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exceptional events. In support of our
disapproval the commenter makes
several arguments: (1) That there is no
statutory or regulatory authority which
allows windblown dust from land that
has been disturbed by human activity to
be considered ‘‘natural;’’ (2) that while
the final rule includes specific language
regarding the treatment of
anthropogenic emissions associated
with fireworks and prescribed burns, it
does not include special provisions for
anthropogenic sources affected by the
wind; (3) that the portion of the
preamble which suggests dust from
anthropogenic sources may be treated as
natural events in certain circumstances
was a drafting error and is legally null;
(4) where the Act does allow for
consideration of human activity, it is
limited to activity that is unlikely to
recur at a particular location and
agriculture does not meet that
definition; and (5) regardless of whether
a high wind event is classified as
‘‘natural’’ or ‘‘human activity,’’ such an
event exists only where the wind is
objectively a ‘‘high wind’’ and
sufficiently high to cause a monitored
violation even in light of the
implementation of whatever measures
are ‘‘necessary’’ to protect public health
under CAA section 319(b)(3)(A)(iv).
Response: Comite’s support for our
decision not to concur with the State’s
exceptional events claims is noted. We
agree with Comite that the events in
question are not due to human activity
that is unlikely to recur and that the
State failed to demonstrate that the
events qualify as natural events.
However our conclusions with respect
to natural events are not based on all of
the legal arguments proffered by the
commenter. We also are not relying on
that portion of the preamble that the
commenter correctly points out is a
legal nullity 82 and instead, where
appropriate, we rely on and cite to other
parts of the preamble regarding natural
events and high winds that remain
applicable. While EPA’s views of the
statute and the EER differ from
Comite’s, we need not address Comite’s
arguments in detail because its intent
was clearly to support the outcome we
have reached regarding the exceptional
events claims.
EE #13: Comite cites additional
support for nonconcurrence with the
State’s 2007 exceptional events requests
beyond what was relied upon by EPA,
namely that wind speeds were not
shown to be ‘‘exceptional’’ for the area
or ‘‘unusual’’ since the State relied on
flawed comparisons to average wind
speeds.
Response: For the 2006 events, the
State did not assert that the winds were
unusually high. For both sets of 2007
events, the evidence provided by the
State did lead EPA to conclude that
winds were unusually high.83 However,
EPA’s 2009 EE decision did not rely on
the State’s conclusions about unusual
winds for any of the exceedances and
we note that this commenter does not
disagree with EPA’s conclusions on the
exceptional events, or with EPA’s
proposed limited disapproval of
Regulation VIII.
4. Clear Causal Relationship
EE #14: Comite agrees with EPA that
the State did not demonstrate there was
a clear causal relationship between the
exceedances and the events that are
claimed to have occurred, as required
under the EER. With regard to the 2007
exceedances, the commenter cites the
lack of sufficiently detailed source
attribution data. With regard to the 2006
exceedances, the commenter concludes
that the proximity and nature of the
thunderstorms that occurred in
northwest Mexico made them ‘‘unlikely’’
to be the cause of the winds at Calexico.
This commenter also believes that the
possibility of any winds associated with
thunderstorm activity north of the
County being the cause of the
Westmorland exceedance is
‘‘problematical at best.’’
Response: Comite’s agreement with
EPA’s 2009 EE decision regarding the
2006 and 2007 exceedances is noted.
EE #15: ICAPCD (Attachment) objects
to EPA’s analysis of a section of the ARB
documentation that compares
September 2, 2006 to other days with
similar meteorological conditions in
order to establish a causal relationship
between the claimed high wind event
and the Calexico exceedances on
September 2, 2006. ICAPCD also rejects
EPA’s concerns regarding the effect of
emissions from OHVs and fallow fields
on the September 2, 2006 Calexico
exceedances. ICAPCD concludes that
EPA’s lack of sound technical
understanding regarding the
meteorological evidence and OHV and
agricultural emissions led EPA to
erroneously reject the State’s finding of
a ‘‘clear causal relationship’’ for the
September 2, 2006 Calexico
exceedances.
Response: In its documentation
supporting its exceptional events
request, the State compared PM10
concentrations on September 2, 2006 to
those on fifteen other days that had
similar meteorology at Calexico.84 The
83 2009
82 NRDC
v. EPA, 559 F.3d 561, 565 (DC Cir. 2009).
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NED, pp. 12–14.
84 September
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PM10 concentrations on most of the days
were low, but on August 18, 2002,
August 19, 2003 and September 2, 2006
the PM10 concentrations were high. The
concentrations on these days in 2002
and 2003 are described in attachments
to the State’s Natural Events
Documentation 85 as being due to
transport from Mexico under high wind
conditions, and these conditions are
stated to be meteorologically different
than the other days at locations other
than Calexico itself. Thus winds at
Calexico were similar for all sixteen
days, but on these specific days the
wind elsewhere and the Calexico
concentrations are higher. The State
considered this to be evidence of an
association or causal relationship
between high wind elsewhere and high
Calexico concentrations.
While we acknowledge that we
misinterpreted the above portion of the
State’s argument in our initial analysis,
our ultimate conclusion remains
unchanged. As we discussed in our
2009 EE decision,86 the State’s argument
is flawed because there were in fact no
high wind measurements on September
2, 2006; instead, the State merely
assumed that wind speeds increased to
the east. As a result, the association
between the winds and concentrations
that was seen for the events in 2002 and
2003 may not reflect what occurred on
September 2, 2006. Thus our original
conclusion is still valid because the fact
remains that ARB’s argument is founded
on speculation. As we explained in our
2009 EE decision,87 such speculation is
not adequate to establish a clear causal
relationship.
Furthermore, as also discussed in our
2009 EE decision,88 significantly lower
PM10 measurements in neighboring
Mexicali contradict ARB’s assertion that
the September 2, 2006 Calexico
exceedances were caused by windblown
dust from a large-scale, regional event
that originated to the south or southeast
of Calexico. Such an event would have
affected both Calexico and Mexicali.
ICAPCD itself concedes that its
explanation for the Calexico
exceedances does not account for the
difference in the PM10 concentrations
85 September NED, p. 12, and Attachment G,
‘‘179B(d) ‘But For’ Analyses—High-Wind Events
from Mexico’’, excerpt from Technical Support
Document: Exclusion of PM10 Measurements in
Excess of the 24–Hour PM10 NAAQS for Imperial
County from 2001 through 2003 Due to Natural
Events and Emissions from Mexico, Volume I of II,
ENVIRON International Corporation, November
2004.
86 2009 EE decision, pp. 11 and 15.
87 Id. at p. 11.
88 Id. at p. 12.
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measured at the Calexico and Mexicali
stations.89
ICAPCD further offers what it
characterizes as the only three possible
explanations for the Calexico
exceedances, and suggests that EPA
should accept the long range transport
argument because it is the most
plausible one.90 To do so would be to
make a decision based on a
predetermined outcome rather than
reliable scientific data that establish a
clear causal relationship as required by
the EER.
ICAPCD’s next objection to our
analysis of ARB’s exceptional event
request with respect to the September 2,
2006 Calexico exceedances is that EPA’s
concern regarding OHV and agricultural
emissions 91 is not relevant because
there are no OHV or domestic
agricultural lands south, southeast or
south-southeast of the Calexico
monitors. EPA disagrees. The September
NED states that the ‘‘source of the PM10
that impacted the Calexico stations
corresponds to lands east and southeast
of the Mexicali stations * * *’’ 92 In fact,
as shown in the TSD for this final
action,93 there is agricultural land
immediately east of Calexico.94 As also
shown in the final TSD,95 the southern
end of the Imperial Sand Dunes OHV
area is also directly east of Calexico,
though it is admittedly farther away.
Thus consideration of these sources was
not inappropriate.
In summary, we are not persuaded by
the above comments and we reject the
allegation that we did not have a sound
technical understanding of the claims
ARB made as to the cause of the
exceedances. We therefore reaffirm our
conclusion that ARB not only failed to
demonstrate that a high wind event
occurred, but also that there was a clear
causal relationship between the alleged
event and the September 2, 2006
exceedances at the Calexico monitoring
stations.
EE #16: ICAPCD (Attachment) states
that EPA mischaracterized some
evidence and inappropriately dismissed
other evidence provided by the State
regarding a causal relationship between
the claimed high wind event and the
Westmorland exceedance on September
89 ICAPCD
Attachment A, Appendix A–1.
90 Id.
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91 2009
EE decision, p. 14.
92 September NED, p. 15.
93 ‘‘Technical Support Document for EPA’s Notice
of Final Rulemaking on Revisions to the California
State Implementation Plan, Imperial County Air
Pollution Control District Regulation VIII—Fugitive
Dust Rules 800–806’’ EPA Region IX, June 2010
(final TSD), Figure 1.
94 Similar land use maps were provided in Figure
3 of both the April and June NEDs.
95 Final TSD, Figure 1.
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2, 2006, and that this led EPA to
erroneously reject the State’s finding of
a clear causal relationship. The
comment has three parts, relating to
alleged EPA mischaracterizations of the
timing of high winds, direction of
thunderstorm travel, and wind
trajectories.
Response: In response to this
comment, we have again reviewed the
wind data provided in the September
NED and, as explained further below,
we believe our original conclusion in
our 2009 EE decision remains correct,
i.e., that the data presented by ARB did
not demonstrate a clear causal
relationship between the claimed high
wind event and the Westmorland
exceedance on September 2, 2006.
The first part of ICAPCD’s comment
focuses on a statement made by EPA
that the increased wind at Oasis toward
Westmorland was simultaneous with
the concentration spike that occurred at
Westmorland during the 19th hour
rather than an hour or two before, as
would be necessary based on the
distance between the two locations.96
We agree with the comment that the
increased wind at Oasis did in fact
occur the hour before the concentration
spike. In addition, we stated that this
wind was directed toward Westmorland
when in fact it was directed toward the
east-northeast.
ARB presented the wind speed and
direction data in a tabular format that is
difficult to interpret.97 To more clearly
articulate why we do not believe these
data show a clear causal relationship
between the event and the exceedance,
we have presented the data in the final
TSD in a visual form that is more
readily understood.98 The arrows
represent the wind directions at Indio,
Oasis, Salton Sea West, and
Westmorland during each of the four
color-coded hours (e.g., all of the yellow
arrows represent the wind direction
during hour 17, etc.). The numbers
above each arrow represent the wind
speed for that hour, and the numbers
below the Westmorland arrows
represent the PM10 concentration. The
data show that the PM10 concentration
spike occurred during hour 19.
ARB claimed that thunderstorm
outflows on September 2, 2006 led to
high wind locally to the northwest and
northeast of Imperial County, and that
dust generated there was carried to
Westmorland. More specifically, ARB
stated the following:
Very high winds were observed at the 17th
and 18th hours north of Imperial County,
PO 00000
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EE decision, p. 16.
NED, Tables 1 and 2, and Figure 19.
98 Final TSD, figure 2.
97 September
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both to the west (in particular at the Oasis
CIMIS station, see Table 1) and to the east
(see measurements at the Blythe, Ripley, and
Palo Verde stations, Table 1). These strong
winds were of very short duration and of
changing direction * * *, consistent with the
collapse of one or several thunderstorm cells
north of Imperial County * * *. Very sharp
peaks in PM10 concentrations were also
observed at the 19th hour at the Brawley and
Westmorland stations (and to a lesser extent
at the Niland station), and appear to be longrange effects of the same events (i.e.
collapsing thunderstorm to the north of
Imperial County) * * *. [A]n analysis of
wind direction at select stations between the
18th and 20th hours indicates that northwest
winds (e.g. 6 p.m. at the SSW and Indio
stations, 7 p.m. at Oasis and Indio, and 8
p.m. at Indio) and east-northeast winds (e.g.
7 p.m. at the Niland and SSE stations) likely
carried air containing elevated PM10
concentrations from areas northwest and
northeast of Imperial County stations toward
the stations.(Emphasis added).99
ARB’s explanation first points to the
‘‘very high’’ winds (of 23.2 mph)
recorded at the Oasis station and the
northwest winds at Salton Sea West
during the 18th hour as factors that
contributed to the exceedance. As a
preliminary matter, we note 100 that no
particular wind speed has been
established as ‘‘high’’ for Imperial
County. Further, winds with an average
speed of 23.2 mph are not what we
would consider ‘‘very high’’ in the
generally accepted meaning of the term.
With the exception of this value, the
data in Figure 2 of our final TSD show
that the winds in this area were not very
elevated.101 We also note that the winds
at Oasis during the 18th hour had a
northerly component rather than a
southerly one, and while it is true that
the winds at Salton Sea West were
blowing toward Westmorland at this
time and that these winds could have
contained some of the dust that may
have been generated in the Oasis area,
the winds at Westmorland were blowing
in almost the opposite direction. It is
thus unclear how much, if any, dust
generated at Oasis during the 18th hour
was actually transported to
Westmorland.
ARB also points to the 7 p.m. winds
at Oasis (hour 19) as a contributing
factor. While these winds were directed
99 September
100 As
NED, pp. 10–11.
we did in our 2009 EE decision, pp. 15 and
19.
101 EPA received comments on its proposed EER
which stated that we should replace the term ‘‘high
winds’’ with the term ‘‘wind-generated dust.’’ In
response to those comments, EPA explained in the
final EER that the Agency chose to retain the
original language because it accurately connotes the
type of natural event that should be excluded under
this rule and it serves as an indicator concerning
the level of wind that caused the exceedance. See
72 FR 13560, 13566.
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toward Westmorland, the winds at
Salton Sea West had a distinct westerly
component so it is not clear that the
winds at Oasis continued on this path
past Salton Sea West. In addition, as for
the previous hour, the winds at
Westmorland were blowing counter to
the wind at Oasis and it is again not
clear that any dust generated north of
Imperial County was transported to
Westmorland during this hour as ARB
claims.
The State finally points to the 8 p.m.
winds at Indio as a contributing factor.
We find it unlikely that these winds
made a significant contribution to the
exceedance at Westmorland given that
they were recorded after the
concentration spike occurred and that
the winds at Oasis, Salton Sea West, and
Westmorland all had northerly
components that ran counter to the
winds at Indio.
As stated in our 2009 EE decision,102
and as ARB stated in the paragraph
quoted above, the winds northwest of
Imperial County (particularly around
the Oasis and Salton Sea West areas)
were variable in speed and direction.
This variability is inconsistent with
ARB’s hypothesis that the winds
remained at an elevated speed and along
a straight line over the 45 mile distance
between Oasis and Westmorland for an
hour or more. Thus it is anything but
clear that dust generated northwest of
Imperial County caused the exceedance
at Westmorland. As a result, EPA’s
minor errors regarding the timing and
direction of the winds at Oasis do not
undermine the Agency’s conclusion that
the contradictory evidence does not
support a finding of a clear causal
relationship.
The second part of ICAPCD’s
comment on the causal relationship
regarding the Westmorland exceedance
argues that the speed and direction of
the increased winds (27.0 mph)
recorded at the Palo Verde station
during hour 17 are consistent with
transport to Westmorland and that the
uncertainty of the precise location of the
thunderstorms in time is not relevant to
a cause and effect analysis. The
commenter further states that EPA does
not appear to argue that the wind speed
or direction is inconsistent with
transport of dust from Palo Verde to
Westmorland.
While we agree with the commenter
that the winds at Palo Verde (which is
separated from Westmorland by a northsouth distance of about 24 miles) were
directed toward Westmorland during
the 17th hour, the winds at
Westmorland were consistently from the
102 2009
south-southeast, southeast, and eastsoutheast directions beginning at the 6th
hour and lasting until the end of the
day. While it is remotely possible that
the winds that occurred at Palo Verde
during the 17th hour led to the transport
of dust to Westmorland, the EER
requires a demonstration of a clear
causal relationship and the limited data
available do not rise to that level.
We also disagree with the commenter
that the location of the thunderstorms
over time is not relevant to a cause and
effect analysis. The EER explicitly
mentions the use of data that show the
relationship in time between the event,
transport of emissions, and recorded
concentrations in exceptional event
demonstrations.103 Furthermore, in this
case, ARB’s basic premise is that
‘‘thunderstorm activity caused strong
outflow winds over areas in close
proximity to Imperial County monitors
* * * [which contributed] to the
elevated PM10 concentrations that were
recorded in Imperial County on that
day.’’ 104 ARB could have attempted to
provide more support for its case by, for
example, considering whether historical
radar data showed thunderstorms were
at various locations around the time the
high winds occurred.
Given the level of uncertainty as to
the cause of the concentration spike at
Westmorland during the 19th hour and
the statutory requirement that EPA’s
exceptional events regulations be based
on the principle that protection of
public health is the highest priority,105
we are again led to the conclusion that
the data before the Agency does not
establish a clear causal relationship
between the exceedance and the event
that is claimed to have occurred.
The third part of ICAPCD’s comment
regarding causal relationship for the
Westmorland exceedance criticizes
EPA’s use of wind trajectories from the
HYSPLIT model since it is expected to
capture the underlying flow pattern but
may not be able to capture the direction
of short-lived high winds that could
transport dust from the north to
Westmorland.
EPA acknowledges that the HYSPLIT
model uses meteorological data with
relatively coarse resolution, e.g., a 40
km grid, and that there may be shortlived or local deviations from the
overall wind flow. However, it remains
true that the HYSPLIT back-trajectories
are inconsistent with transport from
northern stations since they show winds
from the south.106 The HYSPLIT data
EE decision, p. 16.
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103 72
FR 13560, 13573.
NED, p. 2.
105 See CAA section 319(b)(3)(A)(i).
106 2009 EE decision, p. 17.
simply add to the list of inconsistencies
in the State’s explanation. In addition,
ICAPCD’s suggestion that the high
winds were ‘‘short-lived’’ is inconsistent
with ARB’s hypothesis of straight line
transport from the Oasis or Palo Verde
stations for an hour or more over the
45–55 mile distance to Westmorland.
Thus EPA disagrees with this comment.
EE #17: ICAPCD (Attachment) makes
an additional two-part comment about
the causal relationship claim for the
September 2, 2006 exceedances at both
the Calexico and Westmorland
monitoring stations. In order to buttress
its argument that these exceedances
were not the result of recurring
anthropogenic sources within Imperial
Valley, ICAPCD first states that it is
extremely unlikely that all monitors in
the County would simultaneously have
had unusually high PM10 concentrations
if the causes were local to the monitors.
The second part of the additional
comment states that since there were no
high winds throughout Imperial Valley
on September 2, 2006, the cause of the
exceedances could not have been
unpaved roads or agricultural or OHV
land within the Valley.
Response: With respect to the first
part of ICAPCD’s comment, EPA
acknowledged the elevation of PM10 at
all monitors, but did not take a position
on whether the causes were local or
regional.107 Rather, we concluded that a
clear causal relationship had not been
demonstrated since the regional sources
alleged by ARB to be the cause were not
identified. Related to this lack of
identification of the contributing
sources, EPA found that the State did
not demonstrate that the event was not
reasonably controllable or preventable
as there was no attempt to analyze
controls on the non-local sources. Thus
this comment does not affect our
decision to not concur with the State’s
exceptional event claims.
With respect to the second part of
ICAPCD’s comment, as discussed above,
the State argued that high winds
associated with thunderstorm activity
led to the generation of dust north of the
County, which was then transported to
the Westmorland monitor. Even though
agricultural land and other
anthropogenic sources do exist in areas
north of the County including Oasis,108
where the State claimed winds were
high, the State made no attempt to
analyze controls on contributing sources
outside the County in order to address
the EER requirement that the event must
be ‘‘not reasonably controllable or
preventable.’’ Thus, this requirement
104 September
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107 2009
108 See
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was not met even if the commenter’s
arguments regarding transport were
correct. With respect to the Calexico
exceedances, the State speculated that
high winds occurred east and southeast
of Calexico based on extrapolation of a
west to east trend of increasing wind
speed. The same argument could have
been used to conclude that there was
high wind east of Calexico within
Imperial County, including over
agricultural and OHV lands. Therefore
the commenter’s claim that there were
no high winds throughout the Imperial
County is not completely supported by
the State’s own arguments that a high
wind event occurred.
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5. Concentrations in Excess of Normal
Historical Fluctuations
EE #18: Comite cites additional
support for nonconcurrence beyond
what was relied upon by EPA.
Specifically, the commenter states that
numerous monitored exceedances
comparable to those that Imperial
County seeks to exclude from the data
have been measured in the County from
2003–2007. Therefore, the commenter
claims, the concentrations are not ‘‘in
excess of normal historical fluctuations’’
as required by the rule and are not
exceptional events.
Response: EPA’s conclusions about
the requirement that the events be
associated with measured
concentrations in excess of normal
historical fluctuations mainly relied on
the concentrations’ rarity relative to past
measurements. For example, the
September NED states that the 167 μg/
m3 measurement at the Westmorland
station was in the 98th percentile of all
PM10 recordings at that station in the
2001–2007 time period. As explained in
our 2009 EE decision,109 we found
similar evidence that the exceedances
measured on the other days in question
also exceeded normal historical
fluctuations. However, we do agree with
the commenter that the monitoring data
for Imperial County continue to show
violations of the 24-hour PM10 standard.
We believe that improvements to the
ICAPCD’s rules will lead to
improvements in air quality and we
note that this commenter does not
disagree with EPA’s conclusions
regarding the State’s exceptional events
requests, or with EPA’s proposal to
disapprove Regulation VIII.
6. Level of Documentation Required for
EER
EE #19: ICAPCD (Attachment) takes
issue with EPA’s suggestions that
additional data and analysis would have
109 pp.
25–27.
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helped establish causality for the 2006
Westmorland and the 2007 events.
Specifically, ICAPCD states:
Although EPA suggests that higher levels
of documentation for source attribution,
thunderstorm activity, or investigation of
other potential causes would be preferred,
EPA does not suggest reasonable, technically
implementable analyses to achieve these
higher levels of documentation. We would
question what technical analyses EPA
suggests should be conducted. We would
also question whether these analyses and the
required level of data are achievable or
realistic now or in the future for similar
events in Imperial County and in other areas
(particularly those surrounded by remote,
non-populated, non-monitored source areas),
and whether these analyses exceed the
requirements for SIP planning itself. EPA has
not (and, we believe, cannot) propose
reasonable, technically achievable
investigations and analyses superior to those
produced by the District and ARB that would
address EPA’s stated concerns. Thus, we find
that both EPA’s conclusions on causality and
EPA’s position on the level of analysis
required to demonstrate causality are
incorrect and inconsistent with the purpose
of the EER * * *. Such a narrow application
of the EER will preclude states from
excluding from regulatory consideration
exceptional PM data that are completely
inappropriate for inclusion in the normal
planning process.
ICAPCD also includes a table on page
A–8 which cites specific passages of
EPA’s 2009 EE decision pertaining to
source apportionment, satellite imagery,
and consideration of other causes.
Response: Regarding the need for
better source apportionment data, it is
important to identify contributing
sources when evaluating exceptional
event claims involving windblown dust
because it must be demonstrated that
anthropogenic sources contributing to
the exceedances at issue were
reasonably controlled.110 Better source
identification is especially important in
situations where we do not have
confidence that all potential
anthropogenic sources are reasonably
controlled and where there are
exceedances just above the NAAQS
(such as the April 12, 2007 exceedance
at Westmorland) which may have been
preventable with additional controls. In
addition, the inability to identify the
source of the PM emissions associated
with a wind event (i.e., the ‘‘cause’’ of
the dust that led to the exceedance)
110 See, e.g., 2009 EE decision, p. 7 and our
responses to comments EE #s 1 and 4. See also 72
FR 49046, 49051 (August 27, 2007) and 72 FR
13560, 13566, footnote 11, explaining that the
weight of evidence approach to our analysis may
consider winds that produce emissions contributed
to by anthropogenic activities that have been
controlled to the extent possible through use of all
reasonably available reasonable and appropriate
measures.
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hinders our ability to make affirmative
findings that the ‘‘clear causal
relationship’’ and ‘‘but for’’ provisions of
the EER have been satisfied. A Countywide monthly average emission
inventory such as the one used by ARB
that omits some source types (e.g.,
OHVs) is insufficient for these purposes.
While perhaps not required for all
demonstrations, our suggestion for a
wind field and a more highly resolved
inventory are not unreasonable given
ARB’s failure in the present case to
demonstrate that reasonable controls
were in place for contributing sources.
Moreover, a more highly resolved
inventory would provide better support
for any future exceptional events claims
involving Imperial County. Another
method ARB could have potentially
considered for identifying the source of
the emissions and supporting its claim
of a causal relationship is to collect and
examine pollutant species-specific
information. As discussed in the EER
preamble,111 such information may be
available through routine speciation,
monitoring networks, or from selective
laboratory analysis of archived
particulate matter filters for the day
thought to be impacted by an event. In
this case, such an analysis might have
helped ascertain how much of the PM10
that impacted certain monitors was from
agricultural sources versus natural
desert sources.
Regarding ICAPCD’s objection to our
statement that the satellite imagery
provided was not frequent enough to
compare the images with the timing of
the concentration spike at Westmorland
during the 19th hour,112 we note that
ARB could have provided additional
information to supplement the satellite
imagery. Such information could
include, but may not be limited to radar
data and weather observations that note
the presence of blowing dust in areas
around the monitors.
Finally, ICAPCD takes exception to
our desire for better documentation
regarding the investigation of other
potential causes. In this regard, ARB
made the following statement: 113
(ICAPCD) investigated emission generating
activities during this episode, and found that
PM10 emissions for BACM controlled sources
were approximately constant before, during
and after the event. The District determined
that the * * * concentrations of PM10 * * *
were instead primarily the result of windentrained dust * * * associated with a
mesoscale convective system * * *.
Although the preceding passage
suggests that ICAPCD conducted an
111 72
FR 13560, 13573.
EPA decision, pp 17–18.
113 September NED, p. 2.
112 2009
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active investigation of other emission
generating activities on the day of the
event, this claim is largely unsupported
except for an interoffice memo included
in Attachment H to the September NED.
The memo states that various records
were inspected in 2008 but that no
inspections were conducted on the day
of the event. We were thus left
wondering how a file review conducted
two years after the fact qualifies as an
investigation of emission generating
activities ‘‘during [the] episode’’ and
how ICAPCD came to the somewhat
substantial conclusion that emissions
from BACM controlled sources were
constant before, during, and after the
event.
E. OHV Controls
OHV #1: ICAPCD believes that EPA
should have concurred with all of the
exceptional event requests associated
with high winds as discussed in the
Exceptional Events comments
summarized in section II.D above. As a
result, ICAPCD believes that windblown
dust from open areas is not a significant
source category in Imperial County, and
therefore is not subject to the BACM
requirement as part of the SIP.
Response: In our proposed action on
Regulation VIII, we explained why
windblown dust from open areas is
treated as a significant source category
subject to BACM.114 We have not
received information in the comments
or elsewhere that changes this
conclusion or the related decision to not
concur with the State’s exceptional
event requests for Imperial County. See
also responses to Exceptional Events
comments in section II.D above.
OHV #2: CBD comments that BLM
land is the largest PM10 source in
Imperial County and should be subject
to the same controls as adjacent land.
CBD believes the Dust Control Plan
(DCP) requirement for BLM land in Rule
800 section F.5 is unenforceable, in
conflict with the CAA, while other areas
are subject to more stringent Regulation
VIII requirements.
In contrast, ICAPCD believes that Rule
800’s DCP implements BACM, and that
Rule 800’s exemption for BLM does not
relax other Regulation VIII
requirements. For example, Rule 800
section F.5.c requires BLM’s DCP to be
consistent with Rules 804 and 805
except where otherwise prohibited, in
which case section F.5.e requires all
feasible control measures during offroad events. ICAPCD also notes that
where there are such prohibitions,
section F.5.d requires the DCP to
discuss and implement ‘‘other possible
control measures’’ and that Rule 800
section D.3 requires the DCP to be
submitted to ICAPCD, ARB and EPA for
review and comment and to be updated
every two years.
ICAPCD believes BLM should be
treated separately in Regulation VIII
because there are many restrictions
imposed by a variety of laws other than
the CAA that apply to actions on
Federal lands and that the District’s
involvement in these issues would
delay implementation of the PM control
program on BLM lands. ICAPCD also
believes that BLM should be treated
separately because some Federal land
uses preclude traditional dust controls
and because BLM’s OHV areas are far
from Imperial County populations.
ICAPCD argues that even if Rule 800
section F.5.c corresponds to
requirements that are less effective than
those of Rules 804 and 805, such lower
stringency is both necessary and
appropriate given the special nature of
BLM lands.
BLM agrees that many traditional
BACM are not possible on Federal land
because of the large expanses of desert
ecosystems. BLM continues evaluating
the DCP, however, which has led to
closing areas and routes to vehicle use,
restoring closed surfaces to natural
conditions, hardening high traffic areas,
posting and enforcing speed limits,
educating desert users, and controlling
dust from non-OHV activities.
Response: BACM is required but has
not been demonstrated for OHV activity
on BLM land in Imperial County.115
EPA guidance explains that this
demonstration should include
evaluation and documentation of the
technological and economic feasibility
of potential control measures, including
implementation of measures on a
limited basis if full implementation is
not feasible. As stated in our guidance,
‘‘the documentation should compare the
control efficiency of technologicallyfeasible measures, their energy and
environmental impacts and the costs of
implementation.’’ 116 ICAPCD’s
demonstration should include careful
consideration of analogous controls
implemented on private lands in
Imperial County and on public lands in
Maricopa and Clark Counties and
elsewhere, as well as controls
recommended in EPA’s RACM
guidance,117 and suggestions provided
115 Proposal
TSD, pp. 7–8.
Preamble Addendum at 42012–42014.
117 57 FR 18070, 18072.
116 General
114 Proposal
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in our proposal 118 and comments on the
proposal.119
The evaluation of technological
feasibility may appropriately consider
the alleged ‘‘special nature’’ of BLM
lands. Such an evaluation, if conducted
appropriately, may be sufficient to
demonstrate that what constitutes
BACM for BLM land in Imperial County
is different from what constitutes BACM
in other geographical areas and for
private land in Imperial County. The
information provided in the comments
and Regulation VIII submittal, however,
is not sufficient to support such a
distinction. For example, ICAPCD and
other commenters have not
demonstrated how existing BLM
controls implement BACM in the Plaster
City areas, which are open to OHV
activity at all times, and, if such
controls do constitute BACM, why they
cannot be incorporated into Regulation
VIII and the SIP.
Furthermore, with regard to CBD’s
comment concerning the enforceability
of DCPs, State and local requirements
that implement BACM are subject to the
enforceability requirement of CAA
section 110(a). As we stated in our
proposal, BACM has not been
demonstrated for OHV sources because,
among other things, none of the OHV
restrictions are in regulatory form and
submitted for inclusion in the SIP.120
OHV #3: OWD notes that California
State Parks (CSP) manages OHV
recreational activity in Imperial County
at Heber Dunes State Vehicular
Recreation Area, Ocotillo Wells SVRA,
and in an interdepartmental joint
management agreement at the Freeman
Properties immediately north of Ocotillo
Wells SVRA and east of Anza Borrego
Desert State Park. OWD also notes that
Ocotillo Wells SVRA alone represents
approximately 85,000 acres of managed
OHV recreational activity within
Imperial County. While much of this
land is designated trail riding only and
is primarily defined by terrain
constraints, OWD states that the
majority of the area is designated open
riding, where OHVs are not limited to
defined trails. Rather than implement
generalized BACM for OHV activity in
Ocotillo Wells SVRA and other State
Parks, OWD explains that it has adopted
State mandated soil standards, a habitat
monitoring system and other policies
tailored for the case-by-case conditions
found in each park unit. OWD believes
118 See
proposal TSD, pp. 8 and 14–15.
as stated in the General Preamble
Addendum at 42013, ‘‘any control measures that a
commenter indicates during the public comment
period is available for a given area should be
reviewed by the planning agency.’’
120 Proposal TSD, p. 14.
119 Moreover,
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that fencing, and then maintaining, a
vast amount of land is neither
economically nor environmentally
feasible. OWD also believes that
watering, laying gravel, or applying a
chemical solution to the miles of trails
that would be encompassed is neither
economically nor environmentally
feasible. In contrast, CBD argues that
further implementation of Rule 804 and
additional OHV controls may be needed
for State lands including the Ocotillo
Wells SVRA in order to attain air quality
standards.
Response: Rule 804 requires all
persons, including public entities such
as CSP, with jurisdiction over open
areas in Imperial County with over
1,000 square feet of disturbed surface
area to maintain a stabilized surface,
limit opacity to 20% and comply with
at least one of the following: (a) Apply
and maintain water or dust suppressant
to all unvegetated areas; (b) establish
vegetation on all previously disturbed
areas; or (c) pave, gravel or chemically
stabilize.121 OWD’s comment
acknowledges that CSP has jurisdiction
over open areas with over 1,000 square
feet of disturbed surface area within
Imperial County. Because these areas
are not addressed by exemptions in Rule
800 section E or Rule 804 section D,122
these areas must comply with the above
requirements. However, from OWD’s
comment, CSP is clearly not currently
complying with these requirements. As
a result of the inclusion of Rule 804 into
the SIP, these requirements will become
federally enforceable upon the effective
date of this final action, and such
noncompliance could result in civil
action under CAA section 113 and/or
304.
OHV #4: Various commenters argue
that controls suggested in our proposal
as part of the BACM analysis that
ICAPCD still needs to conduct would
not reduce PM10 impacts from OHVs in
Imperial County.
• Many commenters oppose further
restrictions during the summer,
claiming that OHV activity and
emissions are very low in Imperial
County due to high temperatures and
existing red sticker regulations that
restrict certain vehicles during the
summer. BLM concurs that OHV use is
already lowest in the summer, and
ICAPCD also concurs and argues that
OHV restrictions during the summer
would burden public resources without
121 ICAPCD
Rule 804, sections B, C.29, E and F.
also ‘‘Fugitive Dust Control Plan,’’ Bureau
of Land Management El Centro Field Office, June
29, 2006; ‘‘Fugitive Dust Control Plan,’’ Bureau of
Land Management El Centro Field Office, January
25, 2010 Draft; e-mail from Andrew Trouette (BLM)
to Andrew Steckel (EPA), May 24, 2010.
122 See
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reducing emissions. However, one
commenter (0100) states that OHV use
during summer nights is a great activity
which creates minimal dust because
travel is at low speeds on established
trails. Another commenter (0204)
indicates that many promoters run OHV
races at night that allow for fun
recreational activity in cooler
temperatures. This commenter believes
night races decrease risks to spectators
which is more important than reducing
dust emissions. Some commenters also
observe that wind events can occur in
the summer and cause severe dust days.
By contrast, another commenter (0146)
believes that the desert is mainly dry
and free of wind in the summer.
• ICAPCD believes that restrictions
like those in place in Arizona, during
pollution advisory days, would be
unproductive because high-PM forecasts
in Imperial County only occur on highwind days when OHVs are not used.
• Many commenters (e.g., 0094)
observe that OHVs are already restricted
to certain areas, causing crowding and
injuries. ICAPCD notes that OHVs are
restricted to 11% of local BLM land, and
additional closure would probably shift
OHV activity and emissions to other
areas nearby. OWD also believes EPA’s
action could force OHV users to other
areas, causing environmental effects
outside Imperial County.
• ICAPCD comments that EPA cannot
demonstrate that OHV restrictions
would reduce windblown dust
emissions because there is no basis for
EPA’s contention that surfaces impacted
by OHVs would form any appreciable
crust given Imperial’s low level of rain.
OWD similarly comments that crust
repair would be difficult due to the
limited rain in Imperial County.
Another commenter (0120) believes that
restricting OHV areas could increase
PM10 emissions because more vehicles
in smaller areas would disturb more soil
that cannot crust over. See also
comment EE #8.
• OWD comments that fencing,
watering, gravelling or chemically
stabilizing miles of OHV areas is not
feasible. For example, water resources
are scarce and modification of existing
OHV trails could alter natural drainage
patterns and increase erosion.
Response: EPA believes that some of
the information provided in these
comments could be relevant
considerations in the comprehensive
BACM analysis that ICAPCD needs to
undertake in order to determine what
controls constitute BACM for OHV
activity in Imperial County. However, in
general, the comments are conclusory
and not supported by data, detailed
information, or other evidence that
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would be required for an adequate
BACM demonstration under our
guidance.123 As summarized in the
guidance:
In summary, the State must document its
selection of BACM by showing what control
measures applicable to each source category
(not shown to be de minimis) were
considered. The control measures selected
should preferably be measures that will
prevent PM–10 emissions rather than
temporarily reduce them. The documentation
should compare the control efficiency of
technologically-feasible measures, their
energy and environmental impacts and the
costs of implementation.124
Furthermore, contradictions in the
comments also serve to illustrate that
there are fundamental factual questions
that need to be addressed about the
amount of OHV activity during different
seasons and different times of the day,
and the best ways to mitigate emissions
from such activities. At this juncture,
ICAPCD has not conducted an adequate
analysis.
OHV #5: Many commenters (e.g., 0108
and OWD) state that further OHV
restrictions would hurt the already
depressed local economy, and cite
potential effects on local business
owners, farmers, land owners, OHV
users, race car owners, construction
companies, ranchers, the Imperial
Irrigation District and others.
Commenters observe that recreational
activities generate substantial revenue
(0196), and one (0156.1) claims that
OHVs have contributed several hundred
million dollars to the local economy.
ICAPCD believes that the economic cost
of OHV activity restrictions is far more
than appropriate for BACM. For
example, ICAPCD estimates that closing
the Imperial Sand Dunes Recreational
Area would cost $370,000 to $640,000
per ton of PM10 reductions. ICAPCD
provides specific references to support
its cost/benefit analysis. Another
commenter (0219) similarly believes
that additional OHV restrictions, such
as closing land in the summer, would
provide few benefits given the relatively
small emissions from OHVs, but would
have significant economic impacts.
Response: We appreciate the value of
OHV tourism to the local economy, and
agree that ICAPCD must consider
economic feasibility in BACM analyses
evaluating potential controls for
emissions from OHV activities.
However, the relevant inquiry in the
economic feasibility analysis required in
BACM determinations is ‘‘the cost of
reducing emissions from a particular
source category and costs incurred by
123 General
124 Id.
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similar sources that have implemented
emission reductions.’’ 125 In this case,
the cost of OHV restrictions on OHV
area owners (i.e., the State and Federal
governments) and users would appear to
be minimal, and the secondary
economic impacts on businesses
supporting OHV tourism are not
relevant to the required BACM analysis.
In any event, ICAPCD needs to evaluate
the economic feasibility of potential
controls, including those adopted in
other areas, in determining what
controls constitute BACM in this area.
OHV #6: EcoLogic asks EPA to clarify
whether and where OHV restrictions are
being contemplated in the Imperial
Sand Dunes Recreation Area and
elsewhere and to what extent OHV
activity on Federal land is subject to the
proposed rule or ICAPCD jurisdiction.
EcoLogic and another commenter (0141)
also request clarification on which of
the 250 square miles of OHV areas EPA
is asking ICAPCD to evaluate for closure
and what the basis is for claiming that
these areas are likely to impact
populations.
Response: State and Federal agencies
are subject to many local requirements
including Regulation VIII and other air
quality related ICAPCD rules.126 Our
proposal explains why ICAPCD must
analyze whether additional controls
(potentially including closure) are
appropriate for public land in Imperial
County open to OHVs, which ICAPCD
estimates at over 250 square miles.127
We did not identify any specific
geographic areas needing more or less
analysis or control or having more or
less impact on populations. Rather, in
the analysis ICAPCD should consider all
potential available OHV controls in all
OHV areas in Imperial County and,
where feasible, should consider whether
different areas within the County have
different impacts on populations or
areas with exceedances of the NAAQS.
OHV #7: Several commenters believe
additional OHV restrictions should be
analyzed and/or incorporated into
Regulation VIII. CBD believes that OHV
requirements in Rule 804 are too vague
to be enforceable as required by CAA
section 110(a), particularly regarding
BLM and State managed land. CBD
believes Regulation VIII should require
specific BACM measures, such as
restrictions on the number of OHV
vehicles operating each day, to improve
emission quantification and control.
CBD believes such carrying capacity
caps or other restrictions should also
address weather conditions when they
125 General
Preamble Addendum at 42013.
126 See CAA section 116.
127 See, e.g., proposal TSD, pp. 8 and 13–15.
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exacerbate PM10 emissions, such as
during windy weather and the summer.
Comite comments that ICAPCD should
analyze whether OHV permit
requirements, such as those that are
required in San Bernardino County,
should be required in Imperial County.
Comite also believes that ICAPCD
should analyze controls described in the
California State Parks Off-Highway
Motor Vehicle Recreation Division’s
2008 Soil Conservation Standard and
Guidelines.128 Lastly, instead of
decreasing the size of OHV areas, one
commenter (0120) suggested rotating
OHV areas to help surface crust
formation.
Response: The commenters as a group
make constructive suggestions that
would be appropriate for consideration
in a comprehensive evaluation of BACM
for this source category. We believe
ICAPCD should analyze all potential
available OHV controls to meet the
CAA’s BACM requirement, including
those mentioned in the comments and
those adopted in other areas, pursuant
to EPA guidance.129
F. Definition of Disturbed Surface (DS)
DS #1: ICAPCD believes the term
‘‘disturbed surface’’ is self-evident and
that no questions have been raised about
it since rule adoption. ICAPCD believes
Rule 804 is clear that an area is deemed
disturbed if it shows any sign of manmade disturbance (e.g., vehicle traffic)
and the owner/operator cannot prove
that the area meets the characteristics of
a stabilized surface. ICAPCD is willing
to define this term more clearly during
the next revision to Rule 101, but
strongly objects to EPA disapproving
Regulation VIII on this basis. In contrast,
CBD supports EPA’s concerns regarding
this definition in Regulation VIII, and
further believes the definition should be
tailored to Imperial Valley and
explicitly include open areas on BLM
land that emit significant PM10
including the Algodones Dunes. In this
regard, CBD suggests specific edits to
SJVUAPCD’s analogous rule.
Response: We believe the explanation
provided in ICAPCD’s comment is a
logical interpretation of the undefined
term in its regulation. However, we also
believe that alternate definitions are
possible (such as that recommended by
CBD in its comment), and it is common
practice to define all terms used in rules
that are needed in order to ensure
clarity and enforceability. We encourage
ICAPCD to clarify its regulation by
128 Submitted as Exhibit D to Comite comment
letter.
129 See, e.g., General Preamble Addendum at
42012–42013.
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39381
including an appropriate definition of
this critical term and to consider CBD’s
recommendations for the wording of the
rule.
G. Unpaved Road (UR) Controls
UR #1: ICAPCD projects that control
of unpaved non-farm roads provides
55% of Regulation VIII’s emission
reductions. ICAPCD believes this
demonstrates a good faith effort to
reduce PM10 emissions from road
stabilization, and asserts that the County
is trying to increase funding for such
projects. ICAPCD states that the $2
million/year available to the County
Department of Public Works (PWD) for
road maintenance and stabilization
reflects great needs and low availability
of public funds in the County.
According to ICAPCD, this budget is for
maintenance of 1,350 miles of paved
roads which require resurfacing every
10–15 years, or 90 miles of extensive
maintenance each year. Thus, ICAPCD
argues that allocation of 9% of this
budget to stabilize 19 miles of unpaved
road represents, contrary to EPA’s
assertion, the most expedited schedule
possible with the present level of
available funding.
Response: Where economic feasibility
of control depends on public funding,
EPA will consider past funding and the
future availability of funding sources to
determine if a good faith effort is being
made to implement BACM
expeditiously.130 The fact that unpaved
road controls provide 55% of Regulation
VIII’s estimated emission reductions is
not in itself sufficient to demonstrate
good faith efforts to control road dust
expeditiously. Alternatively, for
example, this high percentage of the
total amount of reductions could occur
if other sources are under-controlled or
are less feasible to control. Nonetheless,
EPA believes that some of the
information ICAPCD provides in its
comment on this point could help to
demonstrate a good faith effort to
control road dust expeditiously. Given
ICAPCD and Imperial County’s limited
resources, we do not believe this
analysis needs to be exhaustive, but it
should be more thorough and
documented than presented in the
Regulation VIII submittal and this
comment. For example, ICAPCD
indicates in this comment that the
County is trying to increase funding for
road stabilization but provides no
documentation to help establish this
point. Nor has ICAPCD explained how
the road stabilization budget was
derived in light of various Federal,
130 Proposal TSD, p. 16, and General Preamble
Addendum at 42013.
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State, and local (including local
Measure D) funding sources for public
works construction and maintenance, or
otherwise provided the demonstration
contemplated by the relevant EPA
guidance.131
UR #2: ICAPCD disagrees with EPA
that there could be problems enforcing
Rule 805 section E.7. As evidence,
ICAPCD explains that Imperial County
PWD is meeting its commitment to
implement its submitted plan, which
includes stabilizing different unpaved
roads each year and maintaining all
stabilized roads as intended by the rule.
Response: CAA section 110(a)
requires that control measures be
enforceable. While Rule 805 section E.7
requires that a compliance plan be
submitted to ICAPCD, the rule is not
clear about the specific requirements of
the plan (i.e., that the County must
stabilize different roads each year and
must maintain all stabilized roads) and
does not contain a mandate that the
terms of the plan be carried out.
Evidence that Imperial County PWD is
in fact currently implementing the plan
is not sufficient to ensure enforceability
as required by the CAA.132 ICAPCD
should revise the rule to clarify this
section consistent with enforceability
requirements of CAA section 110(a).
UR #3: Comite believes that ICAPCD
should incorporate additional
restrictions into Regulation VIII,
including property line visible
emissions (VE) limits such as those
adopted by Maricopa County and
SCAQMD, dust controls for unpaved
roads subject to Rule 805 section E.7,
and other more stringent requirements
adopted by SCAQMD, SJVUAPCD,
Maricopa County and Clark County.
Response: ICAPCD’s analysis of
BACM did consider controls
implemented in other areas, including
those adopted by SCAQMD, SJVUACPD,
and Maricopa and Clark Counties. Our
proposal TSD recommends several
specific controls from these areas for
further consideration by ICAPCD,
including imposition of a fence-line
opacity standard.133
However, with the exception of the
deficiencies identified in our proposal,
we believe that ICAPCD sufficiently
analyzed controls in other areas for
potential BACM.134 For example,
ICAPCD explains that SCAQMD has
only a 0% fence-line opacity standard,
whereas ICAPCD and other agencies
with adopted rules approved as BACM
131 See
proposal TSD, p. 16.
id., p. 9.
133 Id., p. 11.
134 2005 BACM analysis, chapter 4, and 2009
PM10 SIP, table 4.2.
132 See
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all have a similar general 20% opacity
standard applicable everywhere, and
not just at the fence-line.135 ICAPCD
claims that SCAQMD’s 0% fence-line
standard is less stringent than a general
20% standard. While it is difficult to
compare the two standards,136 we do
not have evidence that SCAQMD’s
standard is more stringent than the
general standard used by ICAPCD and
by other air districts.
UR #4: One commenter (0154) states
that it is not feasible or cost effective to
eliminate all dust from dirt roads.
Response: We agree with this
comment. Neither Regulation VIII nor
our proposal or this final action assumes
that dust emissions can be completely
eliminated from farm and non-farm dirt
roads.
H. Border Patrol (BP) Controls
BP #1: ICAPCD comments that Rule
800 section F.6.c does not explicitly
exempt BP from fugitive dust controls,
but requires BP to control dust from
roads it owns/operates consistent with
Rule 805 except where inconsistent
with BP’s authority or mission. ICAPCD
indicates that, while BP does not own
any roads, it uses public roads to
accomplish its mission, and some roads
adjacent to the border are used
exclusively by BP. ICAPCD states that
most of these roads are below Rule 805’s
applicability threshold, are located in
remote areas that are for the most part
restricted to BP vehicles, and PM10
controls are not feasible and are
inconsistent with BP’s mission. ICAPCD
explains that although BP neither owns
nor operates these roads, BP is
committed to implement PM10 controls
such as vehicle speed restrictions and
access controls. ICAPCD indicates that
since adoption of Regulation VIII, BP
has submitted two productive DCPs.
Therefore, ICAPCD disagrees with EPA’s
recommendation to remove or narrow
the exemption for BP activities, and
proposes to continue addressing BP
through a DCP requirement to insure
that BP continues controlling fugitive
dust.
Response: First, we note that nothing
in our proposal affects Regulation VIII’s
requirement for BP to develop and
implement DCPs pursuant to Rule 800
sections F.6.a and F.6.b. However,
ICAPCD’s explanation is unclear as to
whether or not BP operates any roads
BACM analysis, p. 21.
example, a 40% opacity plume in the
middle of a large property that disperses to 0%
opacity by the property fence-line violates
ICAPCD’s rule but not SCAQMD’s. Conversely, a
10% opacity plume that disperses to 5% opacity by
the fence-line violates SCAQMD’s rule but not
ICAPCD’s.
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135 2005
136 For
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subject to the rule. If ICAPCD can
support its assertion that BP neither
owns nor operates such roads, the
exemption in Rule 800 section F.6.c. is
simply unnecessary and should be
removed. If BP does own or operate
such roads, we continue to believe that
the exemption is unnecessarily broad
and should be removed or narrowed and
demonstrated to be consistent with
BACM requirements.
ICAPCD offers no evidence or
explanation to support its contention
that Rule 805 requirements are
potentially inconsistent with BP’s
authority and/or mission. We also note
that BP has not raised concerns with our
proposal, although we informed BP of it
before publication. EPA appreciates
BP’s efforts to limit PM10 pollution
through DCPs. Our concern, however, is
with ICAPCD’s Regulation VIII
submittal and the lack of clarity in, and
analysis to support, the actual
provisions in Regulation VIII intended
to govern these activities.
BP #2: OWD comments that BP
frequently goes off-road within Ocotillo
Wells SVRA, beyond OWD’s control.
Response: Rule 804 section E imposes
requirements on owners of open areas
such as Ocotillo Wells SVRA regardless
of who owns vehicles driving on the
open areas. Nothing in our proposal
would affect these existing ICAPCD
requirements.
I. Unpaved Farm Roads and Traffic
Areas (UFRTA) Controls Introduction
The comments summarized in this
section and sections II.J and K relate to
ICAPCD Rule 806, Conservation
Management Practices. In discussing
our proposal regarding Rule 806, a
number of these comments address
various aspects of analogous rules
adopted by State and local agencies in
California and Arizona for controlling
PM10 from agricultural sources. All of
these rules are menu-based and as such
divide the control measures, known as
conservation management practices
(CMPs) or best management practices
(BMP), into three or more menus known
as ‘‘categories.’’ We provide the
following information on these rules as
an introduction to inform our responses
to the comments in this section and
sections II.J and K.
ICAPCD Rule 806, Conservation
Management Practices, is a menu-based
rule that has four categories:
• Land preparation and cultivation.
• Harvesting.
• Unpaved roads.
• Unpaved traffic areas.
All persons who own or operate an
agricultural operation site of forty acres
or more are required to implement one
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CMP from each of these categories.
Table 3 summarizes the relevant
39383
categories from Rule 806 and the other
menu based rules to which we refer:
TABLE 3
State or local agency
Rule
Area
Categories for on-field
agricultural operations
Imperial County APCD (ICAPCD)
806 ..................................
Imperial County ..............
San Joaquin Valley
APCD (SJVUAPCD).
4550 ................................
San Joaquin Valley Planning Area.137
› Land Preparation and
Cultivation (including
tillage).
› Harvesting ..................
› Land Preparation and
Cultivation (including
tillage).
› Harvest .......................
› Cropland—Other.
› Tillage and Harvest ....
Unified
Arizona Department of Environmental Quality (ADEQ).
Arizona Administrative
Code (A.A.C) R18–2–
610 and R18–2–611.
Phoenix Planning
Area.138
Great Basin Unified
(GBUAPCD).
502 ..................................
Alpine, Inyo, and Mono
Counties.139
APCD
South Coast AQMD .....................
Rule 403 And Agricultural Handbook.
South Coast Air
Basin.140
South Coast AQMD .....................
Rule 403 And Coachella
Valley Agricultural
Handbook.
Coachella Valley Planning Area.
› Cropland.
› Land preparation ........
› Harvest .......................
› Other Cultural Practices.
› Active Conservation
Practices.
› Inactive Conservation
Practices.
› Active Conservation
Practices.
Categories for unpaved
Ag. roads and traffic
areas
› Unpaved Roads.
› Unpaved Traffic Areas.
› Unpaved Roads.
› Unpaved Traffic Areas.
› Noncropland.
› Unpaved Roads.
› Unpaved Traffic Areas.
› Unpaved Roads.
› Unpaved Roads.
› Inactive Conservation
Practices.
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We also refer below to SJVUAPCD’s
Rule 8081, Agricultural Sources, which
has opacity and stabilization
requirements for high traffic agricultural
unpaved roads and traffic areas.
UFRTA #1: Comite believes that
California has not demonstrated why
agricultural paved and unpaved roads
should be subject to less stringent
requirements than other roads in
Imperial County (i.e., those subject to
Rule 803 regarding track-out/carry-out
and Rule 805) and cites San Joaquin
Valley where such roads must meet
CMPs as well as general requirements.
137 SJVUAPCD’s jurisdiction includes the entire
counties of San Joaquin, Stanislaus, Merced,
Madera, Fresno, Tulare, and Kings and part of Kern
County. SJVUAPCD does not include the parts of
East Kern that are not in the San Joaquin Valley Air
Basin. See 40 CFR 81.305.
138 The Phoenix Planning Area includes Maricopa
County and a portion of Pinal County. See 40 CFR
81.303.
139 See section 1 and 2 of GBUAPCD Rule 502.
Also see 40 CFR 81.305.
140 SCAQMD’s jurisdiction includes the South
Coast Air Basin and the Coachella Valley Planning
Area. For a description of the boundaries of the Los
Angeles-South Coast Air Basin Area and the
Coachella Valley Planning Area, see 40 CFR 81.305.
The South Coast Air Basin includes all of Orange
County and the more populated portions of Los
Angeles, San Bernardino, and Riverside Counties.
The Coachella Valley Planning Area includes
central Riverside County in the Salton Sea Basin.
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In contrast, ICAPCD and the Farm
Bureau believe Regulation VIII is more
stringent regarding unpaved farm roads
and traffic areas than analogous rules in
other areas even though Imperial
County farm roads and traffic areas are
not subject to opacity limits. These
latter commenters note that Rule 806
requires CMPs for all unpaved roads
and traffic areas regardless of vehicle
trips per day (VTD), unlike SJVUAPCD
Rule 4550. COLAB also explains that
ICAPCD Rule 806 was designed to
address all unpaved roads by applying
to parcels greater than 40 acres (97% of
farmland in Imperial County) compared
to SJVUAPCD’s Rule 4550 which
addresses roads on parcels larger than
100 acres (91% of farmland in the San
Joaquin Valley). Lastly, ICAPCD and the
Farm Bureau assert that most private
unpaved farm roads are less used and
are therefore below Rule 805’s 50 VTD
threshold. Regardless of VTD, however,
these latter commenters argue that
owners of these roads must implement
Rule 806 CMPs.
Response: EPA’s proposal noted that
ICAPCD has not demonstrated BACM
for unpaved farm roads and traffic areas
because of the exemption in Rule 805
section D.2 from opacity and
stabilization requirements applicable to
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non-agricultural operation sites. EPA
further noted that SJVUAPCD does not
provide such an exemption, and
ICAPCD had not justified such an
exemption.141
ICAPCD and other commenters do not
offer evidence that Regulation VIII is as
stringent as comparable controls in this
regard, but instead claim that Regulation
VIII is more stringent in other respects.
For example, no commenter disputes
our conclusion that an unpaved farm
road with 75 VTD would be subject to
opacity standards in SJVUAPCD’s Rule
8081 but not in ICAPCD’s Regulation
VIII. However, ICAPCD and others argue
that the applicability threshold for
unpaved farm roads subject to Rule 806,
for example, is more stringent than
SJVUAPCD’s analogous requirements.
Because opacity and surface
stabilization requirements on heavilyused farm roads and traffic areas are
being implemented in other areas, we
believe that, absent an adequate
explanation, these requirements are at
least presumptively BACM for this
source category in Imperial County.
Accordingly, these controls should be
evaluated as potential BACM by
ICAPCD. However, as stated previously,
ICAPCD may consider conditions
141 Proposal
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specific to Imperial County in a revised
BACM evaluation for unpaved roads
and traffic areas, as appropriate.
We also agree with Comite that it is
not clear why Rule 803 section D.1
exempts farm roads and traffic areas
from certain carry-out and track-out
requirements that apply to similar nonfarm roads. We encourage ICAPCD to
consider removing this exemption,
although such a rule modification is not
mandated by the CAA at this time
because carry-out/track-out has not been
identified as a significant source
category subject to the BACM
requirement.
UFRTA #2: Comite believes that Rule
806’s CMPs are not sufficiently specific
regarding agricultural unpaved roads
and traffic areas. In contrast, ICAPCD
comments that Rule 806 section F.6
requires CMP plans to include other
relevant information, which gives
ICAPCD authority to require adequate
specificity. COLAB also comments that
the CMP forms provided in the rule are
examples and if the relevant
information was provided the form
could be changed.
Response: Issues raised regarding
specificity of CMPs for unpaved roads
and traffic areas are similar to issues
raised regarding the specificity of CMPs
for other agricultural operations. See
response to comment AL #3 below.
J. Agricultural Land Controls (AL)
See Introduction in section II.I above.
AL #1: ICAPCD comments that Rule
806’s CMP requirements are similar to
requirements adopted by SJVUAPCD,
Maricopa County 142 and SCAQMD,143
and are directly based on SJVUAPCD
requirements that EPA approved as
BACM in 2004, citing 69 FR 30035.144
ICAPCD asserts that the individual
CMPs in Rule 806 are similar to those
found in SJVUAPCD Rule 4550 and
GBUAPCD Rule 502 and concludes that
the only differences in the rules are due
to differences in local agricultural
practices. The Farm Bureau also states
that there is little difference between
GBUAPCD and ICAPCD control
measures.
Response: We agree that many
individual CMPs and requirements in
the rules outlined in Table 3 are similar.
However, this overall similarity does
not affect the two specific BACM
deficiencies in ICAPCD Rule 806 for
tilling and harvesting emissions
identified in our proposed action.145
One of these deficiencies concerns the
lack of sufficiently defined requirements
in contrast to the application submittal
and review processes in the SJVUAPCD
and GBUABCD rules that insure more
effective implementation and
enforcement of the requirements.146 The
other deficiency is related to the number
of CMPs required by Rule 806. Rule 806
section E requires one CMP from the
‘‘land preparation and cultivation’’
category and one CMP from the
‘‘harvesting’’ category, while SJVAPCD
Rule 4550 requires an additional CMP
from the ‘‘cropland-other’’ category.
GBUAPCD Rule 502 also requires that
one CMP each be selected from the
‘‘land preparation and cultivation,’’
‘‘harvest,’’ and the ‘‘other cultural
practices’’ categories.147
AL #2: ICAPCD believes that EPA
disregards that Imperial County crops
are irrigated, and that continued
irrigation and conditioning of soil
dramatically reduce its potential for
both entrained and windblown
emissions. ICAPCD believes this fact
must be considered when comparing
Rule 806 to rules in other areas.
Response: As stated previously above,
EPA agrees that it is appropriate to
consider conditions specific to an area
when evaluating potential BACM.148
However, most of the harvested
cropland in other areas subject to
comparable requirements is also
irrigated. The following table shows
data from the 2007 Census of
Agriculture 149 for the total acres of
harvested cropland and the acres of
irrigated harvested cropland in relevant
counties in California and Arizona.
Imperial County and the counties in the
SJVUAPCD 150 are included. Riverside
County in California 151 and Maricopa
County in Arizona are also included.
TABLE 4
Total harvested
cropland
(acres)
County, State
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Imperial, CA .....................................................................................................................................................
Maricopa, AZ ...................................................................................................................................................
Riverside County, CA ......................................................................................................................................
San Joaquin County, CA .................................................................................................................................
Stanislaus, CA .................................................................................................................................................
Merced, CA ......................................................................................................................................................
Madera, CA ......................................................................................................................................................
Fresno, CA .......................................................................................................................................................
142 Although ICAPCD refers to requirements
adopted by Maricopa County in its comments,
Arizona’s rules, A.A.C. R18–2–610 and R18–2–611,
for controlling PM–10 from agricultural sources
apply to some sources beyond the boundaries of
Maricopa County.
143 As noted in Table 3 above, SCAQMD’s Rule
403 has requirements for agricultural activities that
apply to both the South Coast Air Basin and
Coachella Valley Planning Area.
144 EPA approved SJVUAPCD Rule 4550 in 2006,
not in 2004. See 71 FR 7683. EPA approved a
commitment for the San Joaquin Valley CMP
Program in 2004. See 69 FR 30006.
145 See 75 FR 8008, 8011–8012.
146 See SJVUAPCD Rule 4550 section 6.3 and 6.4
and GBUAPCD Rule 502 section 6.3 and 6.4.
147 See SJVUAPCD Rule 4550 section 6.2 and
SJVUAPCD ‘‘List of Conservation Management
Practices.’’ See also GBUAPCD Rule 502 section 6.2
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and, for example, GBUAPCD Supplemental
Application Form for Alfalfa. See also
‘‘Conservation Management Practices for Farms in
Inyo, Mono and Alpine Counties, Program
Description and Plan Application Forms,’’
December 19, 2008, Great Basin Unified Air
Pollution Control District, at https://
www.gbuapcd.org/farm/
CMPprogramdescriptionandforms.pdf.
148 General Preamble Addendum at 42010 and
42012.
149 2007 Census of Agriculture, California, State
and County Data, and 2007 Census of Agriculture,
Arizona, State and County Data, United States
Department of Agriculture, National Agricultural
Statistics Service. See https://
www.agcensus.usda.gov/Publications/2007/
Full_Report/Volume_1,_Chapter_2_County_Level/
California/cav1.pdf and https://
www.agcensus.usda.gov/Publications/2007/
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Fmt 4701
Sfmt 4700
375,904
190,182
163,783
444,670
307,992
466,304
264,767
978,948
Irrigated
harvested
cropland
(acres)
375,167
189,141
158,437
426,670
297,053
458,017
260,596
960,215
Full_Report/Volume_1,_Chapter_2_County_Level/
Arizona/azv1.pdf.
150 See footnote 141 above. The census data in
Table 4 are for all of Kern County.
151 Of all the counties included in SCAQMD,
Riverside County has the largest acreage of
harvested cropland. According to the 2007 Census
of Agriculture, Orange County has 7,846 acres of
harvested cropland, Los Angeles County has 25,829
acres of harvested cropland, San Bernardino County
has 27,516 acres of harvested cropland, and
Riverside County has 163,783 acres of harvested
cropland. 2007 Census of Agriculture, California,
State and County Data, United States Department of
Agriculture, National Agricultural Statistics
Service. See https://www.agcensus.usda.gov/
Publications/2007/Full_Report/
Volume_1,_Chapter_2_County_Level/California/
cav1.pdf.
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39385
TABLE 4—Continued
Total harvested
cropland
(acres)
County, State
Kings, CA .........................................................................................................................................................
Tulare, CA ........................................................................................................................................................
Kern, CA ..........................................................................................................................................................
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Thus, the mere fact that crops are
grown using irrigation in Imperial
County does not in and of itself justify
different standards for BACM.
AL #3: ICAPCD comments that Rule
806 section F.6 specifies that the CMP
plan shall include ‘‘other relevant
information as determined by the
ICAPCD,’’ which gives ICAPCD
authority to modify the CMP plans to
specify frequency of CMP applicability.
Therefore ICAPCD believes a
mechanism is in place in the rule for
modification of CMPs to provide such
details, and therefore this should not be
a basis for disapproval of Regulation
VIII as BACM. ICAPCD notes its
commitment to modify the CMP plans
to provide such details.
Response: As noted by ICAPCD, Rule
806 section F.6 provides a mechanism
that could be used by ICAPCD to
provide greater specificity. However
there is no required process in the rule
for sources to provide such information
to ICAPCD or for ICAPCD to review the
CMPs and/or to require revision of the
CMPs that sources have chosen to
implement. Under section F, sources are
only required to prepare a plan
containing minimal information and to
maintain a copy of the plan. Thus the
CMPs would continue to be broadly
defined unless or until ICAPCD
proactively determines that greater
specificity is needed. Absent such vital
details, it would be difficult for
regulated entities to know precisely
what is required of them to comply with
a BACM level of control, and it would
be difficult for ICAPCD, EPA, or others
to enforce these requirements.152 In
152 For instance, one of the CMPs that is both in
the ‘‘land preparation and cultivation’’ category in
Rule 806 section E.1 and the ‘‘harvesting’’ category
in section E.2 is ‘‘equipment changes/technological
improvements’’ which is defined in section C.15 as
‘‘To modify the equipment such as tilling; increase
equipment size; modify land planning and land
leveling; match the equipment to row spacing;
granting to new varieties or other technological
improvements. It reduces the number of passes
during an operation, thereby reducing soil
disturbance.’’ This definition is too broad to ensure
enforceability. Moreover, because there is no
mechanism to narrow the definition for a particular
agricultural operation, a CMP may be implemented
in a manner less stringent than a BACM level of
control. In a similarly broad fashion, Rule 806
section C.34 defines ‘‘speed limits,’’ a CMP in both
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contrast, SJVUAPCD Rule 4550 section
5 requires sources to prepare and submit
a CMP application to the District for
approval and section 6 requires the
District to evaluate and either approve
or disapprove the application in writing.
GBUAPCD Rule 502 sections 5 and 6
contain substantially identical
requirements. Such requirements
provide a mandatory process that is far
more likely to ensure that the CMPs are
implemented and enforceable at a
BACM level of control than the
provision in ICAPCD Rule 806.
Finally, even if ICAPCD were to
routinely exercise its discretionary
authority in Rule 806 to specify the
frequency of CMP applicability, the
deficiency noted in our proposed action
related to lack of CMP specificity
extends beyond the issue of
frequency.153
AL #4: ICAPCD claims that BACM
should not be required for harvest
activities because the emissions from
these activities (0.01 tpd) are negligible.
ICAPCD argues that efforts to increase
regulation of emissions from harvesting
would waste resources. In addition,
ICAPCD claims that the CMPs in Rule
806 related to harvesting are similar to
those in SJVUAPCD Rule 4550.
Response: ICAPCD has identified
tilling emissions as a significant
source.154 As stated in our proposal for
this action, measures in Rule 806 for
harvesting must also meet BACM
because the activities occur at the same
facilities and are integrally related to
tilling emissions.155 By analogy, where
enforceable volatile organic compound
(VOC) reasonably available control
technology (RACT) level controls are
required for refineries, SIP rules
generally impose leak detection and
repair requirements on valves, flanges,
threaded connections and other related
the ‘‘unpaved roads’’ category in section E.3 and the
‘‘unpaved traffic areas’’ category in section E.4, as
‘‘enforcement of speeds that reduce visible dust
emissions. The dust emissions from unpaved roads
are a function of speed, meaning reducing speed
reduces dust.’’ However, an appropriate speed limit
or range of speed limits is not specified or
otherwise insured.
153 See 75 FR 8008, 8011–8012.
154 Proposal TSD, pp. 5–6.
155 Proposal TSD, p. 10, footnote 25.
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419,964
560,320
764,929
Irrigated
harvested
cropland
(acres)
419,080
540,887
756,645
equipment even if emissions from any
one of these taken individually might be
much smaller than the major source
threshold requiring RACT.156
We agree that individual CMPs for
emissions from harvesting activities in
Rule 806 are generally similar to CMPs
for such emissions in the San Joaquin
Valley. However, both SJVUAPCD and
GBUAPCD require one more CMP for
on-field agricultural sources than does
Rule 806.157 This additional CMP may
reduce emissions from harvesting
activities. ICAPCD must establish that
requiring fewer controls for on-field
agricultural activities is consistent with
BACM requirements. Thus far ICAPCD
has not provided a convincing
justification.
AL #5: ICAPCD disagrees with our
identification of the requirements of
Rule 806 for tilling as a deficiency in the
BACM analysis. In support of its
position, ICAPCD asserts that San
Joaquin Valley sources may select two
CMPs that reduce emissions from tilling
from the list of measures, but they are
not required to do so. ICAPCD also
claims that because per-acre emissions
from land preparation are about four
times as high in the San Joaquin Valley
as they are in Imperial County, the costeffectiveness of emission reductions
from tilling activities through the
implementation of any CMP should be
four times as high in Imperial County as
in the San Joaquin Valley. For these two
reasons, ICAPCD believes that Rule 806
requirements for tilling are as stringent
as analogous SJVUAPCD requirements.
In contrast, Comite comments that
Arizona Rules 18–2–610 and 611
require at least two CMPs from each
156 SJVUAPCD Rule 4451, Valves, Pressure Relief
Valves, Flanges, Threaded Connections and Process
Drains at Petroleum Refineries and Chemical Plants,
amended April 20, 2005.
157 See SJVUAPCD Rule 4550 section 6.2 and
SJVUAPCD ‘‘List of Conservation Management
Practices.’’ See also GBUAPCD Rule 502 section 6.2
and, for example, GBUAPCD Supplemental
Application Form for Alfalfa. See also
‘‘Conservation Management Practices for Farms in
Inyo, Mono and Alpine Counties, Program
Description and Plan Application Forms,’’
December 19, 2008, Great Basin Unified Air
Pollution Control District, at https://
www.gbuapcd.org/farm/
CMPprogramdescriptionandforms.pdf.
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category in the rule whereas Rule 806
requires only one, and that SJVUAPCD
requires up to three CMPs.
Response: Although ICAPCD focuses
here on emissions from tillage, the
deficiency in our proposed rule is
related to requirements in Rule 806 for
sources to implement one fewer CMP
overall for on-field agricultural sources
than is required by SJVUAPCD Rule
4550 and GBUAPCD Rule 502. Thus the
fact that sources subject to SJVUAPCD
Rule 4550 are not required to select two
CMPs for reducing emissions from
tillage is irrelevant. ICAPCD needs to
assess whether additional CMPs for onfield agricultural sources are BACM for
Imperial County.
ICAPCD has not established that the
agricultural activities in Imperial
County are significantly different from
those in other areas. Accordingly, EPA
believes that ICAPCD should have
BACM level controls for both tillage and
harvest emissions as do other areas with
programs for emissions from
agricultural activities, and should
consider SJVUAPCD and controls from
other areas with analogous rules when
assessing whether a requirement for
additional CMPs would be economically
and technologically feasible to control
emissions from these activities. ICAPCD
claims that implementing tillage CMPs
may be more cost-effective in the San
Joaquin Valley, but does not address
whether it would be economically
feasible to require additional CMPs in
Imperial County.
We agree with Comite that sources
subject to Arizona Rules 18–2–610 and
611 are required to implement two
practices each from the ‘‘tillage and
harvest’’ and ‘‘cropland’’ categories.
ICAPCD needs to consider whether
requiring four practices for on-field
agricultural sources constitute BACM
for Imperial County.
AL #6: Comite claims that Maricopa’s
inspection regime for agricultural
sources is more rigorous than ICAPCD’s.
Response: Comite provides no
supporting information on either the
Maricopa County or ICAPCD inspection
program on which to base a response
and we are not otherwise aware of
information that supports this comment.
AL #7: The Farm Bureau agrees that
SJVUAPCD requires an additional CMP
from the ‘‘cropland-other’’ category but
notes that the same requirement is
found in ICAPCD’s ‘‘land preparation
and cultivation’’ and ‘‘harvest activities’’
categories. As a result, the Farm Bureau
believes that including an additional
category would be redundant and
onerous for participants.
Response: The deficiency identified
in our proposed action is related to the
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requirement in Rule 806 for Imperial
County sources to implement one fewer
practice for on-field agricultural sources
overall without a sufficient
justification.158 ICAPCD does not
necessarily need to add a category to
Rule 806 in order to address this
deficiency. For example, depending on
what is most appropriate for conditions
in Imperial County, ICAPCD may be
able to require that more than one CMP
be implemented from the categories that
currently exist in Rule 806. Moreover, it
would not be redundant to require
Imperial County sources to implement
an additional CMP for on-field
agricultural sources. Rule 806 has two
categories for on-field agricultural
sources, ‘‘land preparation and
cultivation’’ and ‘‘harvesting,’’ and
requires sources to implement one
practice from each category. As noted in
Table 3 above, SJVUAPCD Rule 4550
and GBUAPCD Rule 502 have three
categories for on-field agricultural
sources, and require that sources
implement one practice from each of
these categories. Moreover, as noted in
our response to comment AL #5 above,
sources subject to Arizona Rules 18–2–
610 and 611 are required to implement
four practices for on-field agricultural
sources. As part of a BACM analysis,
ICAPCD should consider the economic
and technological feasibility of requiring
additional CMPs for on-field
agricultural sources, including
consideration of the requirements in
rules adopted by SJVUAPCD, GBUAPCD
and Arizona.
K. Agricultural Land Windblown Dust
Controls (ALWD)
See Introduction in section II.I above.
ALWD #1: COLAB comments that the
deficiencies identified by EPA related to
windblown dust are particularly
troublesome because they are so
surprising. COLAB believes that Rule
806 exceeds CAA needs because
windblown dust from agriculture is
insignificant. Comite, on the other hand,
notes SCAQMD’s requirements for
reducing windblown dust from active
and inactive agricultural fields as BACM
measures that ICAPCD should consider
along with recommendations in U.S.
Department of Agriculture’s (USDA)
National Agronomy Manual for
reducing such dust.
Response: EPA has determined that
windblown dust from agriculture is a
significant PM10 source category in
Imperial County for which ICAPCD
must demonstrate, but has not yet
demonstrated, implementation of BACM
PO 00000
level controls.159 ICAPCD should
include in its BACM analysis
consideration of whether existing
SCAQMD controls, among others, and
USDA recommendations for controlling
wind erosion, are economically and
technologically feasible measures to
reduce windblown dust from active and
fallow agricultural fields. Also see
response to comment General #3 above.
ALWD #2: ICAPCD believes that EPA
should have concurred with exceptional
event requests associated with high
winds as discussed in the exceptional
event comments above. As a result,
ICAPCD believes that windblown dust
from agricultural lands is not a
significant source category in SIP
development, and therefore not subject
to BACM.
Response: In our proposed action on
Regulation VIII, we explained how we
determined that windblown dust from
agricultural lands is a significant source
category subject to BACM.160 We have
not received information in the
comments or elsewhere that affects this
conclusion or the related 2009 EE
decision. See also responses to
exceptional event comments above and
comment OHV #1.
ALWD #3: ICAPCD disagrees that Rule
806 does not apply to fallow agricultural
fields. ICAPCD states that there are no
exemptions in Rule 806 for fallow fields
and fallowing is an optional CMP to
control emissions from ‘‘land
preparation and cultivation’’ under Rule
806 section E.1.
Response: Fallowing land is defined
in Rule 806 section C.16 as ‘‘Temporary
or permanent removal from production.
Eliminates entire operation/passes or
reduces activities.’’ We note that the
fallowing CMP is an option under both
the ‘‘land preparation and cultivation’’
category in section E.1 and the
‘‘harvesting’’ category in section E.2.
While the fallowing CMP in Rule 806
section E.1 may reduce emissions from
‘‘land preparation and cultivation’’ and
from ‘‘harvesting,’’ it does not address
any windblown dust emissions that may
occur once a field is removed from
production. EPA believes that the
evaluation of BACM level controls for
windblown dust from fallow fields
should include consideration of USDAapproved conservation systems and
activities.161
ALWD #4: ICAPCD comments that
ICAPCD farms are all irrigated and
historically well watered, which leads
to stable clods and/or aggregates that
lower susceptibility to wind erosion
159 Proposal
TSD, pp. 10–11.
pp. 5–7.
161 Id., pp. 10–11 and 17.
160 Id.,
158 75
FR 8008, 8012.
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consistent with USDA’s National
Agronomy Manual. ICAPCD estimates
that long-term irrigation reduces PM10
emissions by 25–45% from the
predominant cultivated soil types in
Imperial County, so local fallow and
active agricultural land is controlled for
windblown emissions relative to land
not previously used for irrigated
agriculture. In contrast, ICAPCD
believes that SCAQMD’s farm acreage is
overwhelmingly devoted to dryland
grain farming, and EPA has not shown
that SCAQMD controls are appropriate
for ICAPCD’s irrigated fields.
Response: Based on data in Table 4,
EPA believes that the majority of
ICAPCD harvested acreage is irrigated.
However, EPA disagrees that farm
acreage subject to SCAQMD controls is
overwhelmingly devoted to dryland
farming. See total harvested cropland
acres and irrigated harvested cropland
acres for Riverside County in Table 4.
While historic irrigation may provide
for some level of control, windblown
dust from agriculture is a significant
source, and ICAPCD is required to
implement BACM level controls for
windblown emissions from active and
fallow agricultural fields. ICAPCD has
not provided a convincing justification
for why controls in the Coachella Valley
Planning Area are not applicable to
Imperial sources. ICAPCD’s evaluation
for BACM level controls for windblown
dust from agricultural sources should
include requirements in SCAQMD Rule
403 and the Coachella Valley
Agricultural Handbook.
ALWD #5: ICAPCD notes that winds
above 25 mph are extremely rare in the
agricultural portion of Imperial Valley,
and farmers usually avoid tilling on
windy days to conserve soil. As a result,
ICAPCD does not believe that
SCAQMD’s restriction for soil
preparation and maintenance during
days with winds above 25 mph would
impact windblown dust emissions from
agricultural fields in Imperial County. In
contrast, Comite points to SCAQMD’s
requirements as potential BACM that
ICAPCD has not properly considered.
Response: ICAPCD must analyze and
implement BACM for agricultural
windblown dust emissions.162 Such
analysis may consider whether a
restriction on tilling activities on days
with winds above 25 mph is appropriate
in Imperial County pursuant to our
guidance.163 However, ICAPCD has not
provided such analysis in the
Regulation VIII submittal, its comments
or elsewhere. To the extent that farmers
avoid tilling on windy days to conserve
162 Proposal
163 General
TSD, pp. 5–7.
Preamble Addendum at 42013.
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soil anyway, this restriction would not
seem to be onerous.
ALWD #6: ICAPCD comments that
SCAQMD’s only additional requirement
for active fields besides the restriction
on tilling on days with winds above 25
mph is to implement one more CMP
from a list that includes minimum
tillage. ICAPCD believes this CMP is not
directly effective at reducing
windblown emissions, and hence
ICAPCD believes that by EPA’s own
reasoning, this requirement does not
require windblown control on active
fields in the South Coast Basin.
Response: ICAPCD has not explained
why minimum tillage would not
directly reduce windblown dust from
active fields. EPA expects that
minimum tillage would reduce
windblown emissions by maintaining
more plant residue on the field than
conventional tillage. Establishing and
maintaining land cover is one of the five
principles noted in the National
Agronomy Manual for wind erosion
control.164
ALWD #7: Comite believes that more
specificity and information must be
provided concerning IID’s Fallowing
Program to ensure that emission
reductions from it are quantifiable,
verifiable and enforceable.
Response: ICAPCD must analyze and
implement BACM for agricultural
windblown dust emissions.165 If, as a
result of this analysis, ICAPCD
concludes that IID’s Fallowing Program
is needed to implement BACM, then we
agree that ICAPCD needs to provide
more information about IID’s program
and ensure that controls that are
provided through the program are
enforceable.
ALWD #8: Regarding EPA concerns
with agricultural windblown dust
controls, ICAPCD and the Farm Bureau
note that Rule 806 was modeled after
EPA-approved SJVUAPCD Rule 4550 at
EPA’s recommendation.
Response: EPA’s guidance provides
that BACM is determined on a case-bycase basis and can consider the specific
conditions of the nonattainment area.166
When we approved SJVUAPCD Rule
4550, we did not believe that
SJVUAPCD had a regular and repeated
windblown dust problem.167 However,
ICAPCD asserts in its 2009 PM10 Plan
that the ‘‘overwhelming majority of
airborne PM in Imperial County is
primary PM. The major source of
164 See p. 502–17 of the USDA NRCS National
Agronomy Manual, October 2002.
165 Proposal TSD, pp. 5–7.
166 See General Preamble Addendum at 42010
and 42012.
167 See, e.g., 73 FR 14687, 14693 (March 19,
2008).
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39387
primary PM is fugitive windblown dust
* * *.’’ 168 Moreover, ICAPCD’s 2009
PM10 Plan discusses how the flat terrain
of Imperial Valley and strong
temperature differentials produce
moderate winds and how Imperial
County occasionally experiences high
winds with speeds greater than 30 mph
in April and May. In addition, the 2009
PM10 Plan attributes monitored
exceedances in September and June to
high winds.169 As a result, EPA believes
that ICAPCD must consider windblown
dust controls for agricultural sources.
Also, see responses to comments
General #3 and EE #5.
ALWD #9: The Farm Bureau notes
that both Rule 806 and the ‘‘Agricultural
Air Quality Conservation Management
Practices for Imperial Valley’’ were
developed consistent with rules adopted
in other areas and EPA
recommendations. As a result, the Farm
Bureau believes that this ensured Rule
806 was adequate.
Response: See response to comment
General #3.
L. Other Controls (OC)
OC #1: Comite believes Regulation
VIII should be further strengthened by
removing director’s discretion in Rule
802 section D.1, and removing the
exemption in Rule 802 section D.4.
ICAPCD objects to EPA’s concerns
regarding Rule 802 section D.1 because:
(1) The APCO’s discretion is limited to
a determination of whether any of the
controls in sections F.1 through F.3 can
be implemented to satisfy the 20%
opacity and stabilized surface
requirements; (2) where a SIP-approved
rule provides APCO discretion, the
APCO can exercise the discretion
without further SIP-approval; and (3)
EPA has final enforcement authority for
SIP-approved rules.
Response: EPA believes that the
director’s discretion provisions in Rule
802 are generally not acceptable under
the CAA. Regarding ICAPCD’s first
argument, Rule 802 section D.1 provides
the APCO discretion to waive
completely the opacity and stabilized
surface requirements without limiting
discretion either by a procedure that the
APCO must use (e.g., test method X) or
by boundaries to the discretion (e.g., up
to 30% opacity instead of 20% opacity).
Thus, the discretion is not ‘‘limited.’’
Regarding ICAPCD’s second
argument, we note initially that EPA has
a long history of rejecting such broad
APCO discretion in SIP rules.170
168 2009
PM10 SIP, p. 1–1.
PM10 SIP, pp. 1–3 and 2–4.
170 See, e.g., ‘‘Guidance Document for Correcting
Common VOC and Other Rule Deficiencies,’’ U.S.
169 2009
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Moreover, we limit such discretion
precisely because the APCO can
exercise it without further SIP approval
where a SIP-approved rule provides
APCO discretion.
Regarding ICAPCD’s third argument,
while we can enforce SIP-approved
rules, as stated, director’s discretion
provisions undermine their
enforceability because enforcement of
the rules are constrained by their terms.
In this case, EPA or others could be
restricted in enforcing against activity
exempted by the APCO if this provision
were SIP-approved.
While we share Comite’s concerns
with Rule 802 section D, our limited
disapproval with respect to Rule 802
section D will not trigger sanctions or a
FIP obligation because Rule 802 does
not address a source category identified
as significant and thus requiring BACM
at this time. Therefore our limited
disapproval will not trigger sanctions
under CAA section 179 or a FIP
obligation under section 110(c) with
respect to bulk materials regulated by
Rule 802. However, should regulation of
bulk materials be subject to the BACM
requirement in the future or to meet
other SIP planning requirements under
CAA title I, part D such as reasonable
further progress or attainment, the
APCO discretion in Rule 802 section D.1
or the exemptions in Rule 802 section
D.4 could result in such consequences
and/or affect the emission reduction
credit for the rule.
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M. Statutory and Executive Order
Reviews (SEO)
SEO #1: OWD believes that EPA
should address Executive Order 12898,
which requires Federal agencies to
identify and address disproportionately
adverse health or environmental
impacts on minority and low-income
populations. Specifically, OWD believes
that EPA’s action may impact Imperial
County’s Hispanic and low-income
population by reducing tourist income
from OHV users. In contrast, Comite
applauds the commitment of the
Regional Administrator of EPA Region 9
to environmental justice principles, and
notes that relatively large portions of the
population in this area are not only
Hispanic and poor, but are also suffering
from poor health and this is exacerbated
by air pollution problems in this area.
Response: EPA agrees it is important
to consider environmental justice in our
actions and we briefly addressed
environmental justice principles in our
EPA Region IX, August 21, 2001 (the Little
Bluebook); and ‘‘Issues Relating to VOC Regulation
Cutpoints, Deficiencies, and Deviations,’’ U.S. EPA,
OAQPS, May 25, 1998 (The Bluebook).
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proposal TSD.171 Executive Order
12898, ‘‘Federal Actions to Address
Environmental Justice in Minority
Populations and Low-Income
Populations’’ (February 16, 1994)
establishes Federal executive policy on
environmental justice. Its main
provision directs Federal agencies, to
the greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies and activities on minority
populations and low-income
populations in the United States. The
Executive Order has informed the
development and implementation of
EPA’s environmental justice program
and policies. Consistent with the
Executive Order and the associated
Presidential Memorandum, the
Agency’s environmental justice policies
promote environmental protection by
focusing attention and Agency efforts on
addressing the types of environmental
harms and risks that are prevalent
among minority, low-income and Tribal
populations.
This action will not have
disproportionately high and adverse
human health or environmental effects
on minority, low-income or Tribal
populations because it increases the
level of environmental protection for all
affected populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population.
Specially, EPA’s limited approval and
limited disapproval of Regulation VIII
would have the affect of strengthening
environmental requirements throughout
ICAPCD, and would not relax
environmental requirements in any area.
Thus it promotes environmental justice
by increasing the level of human health
and environmental protection for an
area where, as the commenters note,
relatively large portions of the
population are low income and/or
minority.
SEO #2: OWD notes that EPA’s action
may be subject to NEPA evaluation.
Response: EPA actions under the CAA
are exempt from NEPA.172
SEO #3: OWD believes that EPA
should address increased management
costs for Imperial County’s OHV
recreation areas and the effects on OHV
areas outside Imperial County. As a
result, OWD does not believe that EPA
has a basis to claim (regarding the
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III. EPA Action
No comments were submitted that
change our assessment of Regulation
VIII as described in our proposed action.
Therefore, as authorized in sections
110(k)(3) and 301(a) of the Act, EPA is
finalizing a limited approval of the
submitted rules. This action
incorporates the submitted rules into
the California SIP, including those
provisions identified as deficient. As
authorized under section 110(k)(3), EPA
is simultaneously finalizing a limited
disapproval of the rules. As a result,
sanctions will be imposed in Imperial
County unless EPA approves
subsequent SIP revisions that correct the
rule deficiencies within 18 months of
the effective date of this action. These
sanctions will be imposed under section
179 of the Act according to 40 CFR
52.31. In addition, EPA must
promulgate a Federal implementation
plan (FIP) under section 110(c) unless
we approve subsequent SIP revisions
that correct the rule deficiencies within
24 months. Note that the submitted
rules have been adopted by ICAPCD,
and EPA’s final limited disapproval
does not prevent the local agency from
enforcing them.
IV. Statutory and Executive Order
Reviews
A. Executive Order 12866, Regulatory
Planning and Review
The Office of Management and Budget
(OMB) has exempted this regulatory
action from Executive Order 12866,
entitled ‘‘Regulatory Planning and
Review.’’
B. Paperwork Reduction Act
This action does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. Burden is
defined at 5 CFR 1320.3(b).
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to conduct
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements unless the
171 Proposal
172 See
TSD, p. 3.
40 CFR 6.101(b).
Unfunded Mandates Reform Act), that
no additional costs result from this
action.
Response: As explained in our
proposal, our action would approve and
disapprove pre-existing requirements
under State or local law, and impose no
new requirements. Accordingly, no
additional costs to State, local, or tribal
governments, or to the private sector,
result from this action.173
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agency certifies that the rule will not
have a significant economic impact on
a substantial number of small entities.
Small entities include small businesses,
small not-for-profit enterprises, and
small governmental jurisdictions.
This rule will not have a significant
impact on a substantial number of small
entities because SIP limited approvals
and limited disapprovals under section
110 and subchapter I, part D of the
Clean Air Act do not create any new
requirements but simply approve and
disapprove requirements that the State
is already imposing. Therefore, because
this limited approval and limited
disapproval action does not create any
new requirements, I certify that this
action will not have a significant
economic impact on a substantial
number of small entities.
Moreover, due to the nature of the
Federal-State relationship under the
Clean Air Act, preparation of flexibility
analysis would constitute Federal
inquiry into the economic
reasonableness of State action. The
Clean Air Act forbids EPA to base its
actions concerning SIPs on such
grounds. Union Electric Co., v. U.S.
EPA, 427 U.S. 246, 255–66 (1976); 42
U.S.C. 7410(a)(2).
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D. Unfunded Mandates Reform Act
Under sections 202 of the Unfunded
Mandates Reform Act of 1995
(‘‘Unfunded Mandates Act’’), signed into
law on March 22, 1995, EPA must
prepare a budgetary impact statement to
accompany any proposed or final rule
that includes a Federal mandate that
may result in estimated costs to State,
local, or tribal governments in the
aggregate; or to the private sector, of
$100 million or more. Under section
205, EPA must select the most costeffective and least burdensome
alternative that achieves the objectives
of the rule and is consistent with
statutory requirements. Section 203
requires EPA to establish a plan for
informing and advising any small
governments that may be significantly
or uniquely impacted by the rule.
EPA has determined that the limited
approval and limited disapproval action
promulgated does not include a Federal
mandate that may result in estimated
costs of $100 million or more to either
State, local, or tribal governments in the
aggregate, or to the private sector. This
Federal action approves and
disapproves pre-existing requirements
under State or local law, and imposes
no new requirements. Accordingly, no
additional costs to State, local, or tribal
governments, or to the private sector,
result from this action.
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E. Executive Order 13132, Federalism
Federalism (64 FR 43255, August 10,
1999) revokes and replaces Executive
Orders 12612 (Federalism) and 12875
(Enhancing the Intergovernmental
Partnership). Executive Order 13132
requires EPA to develop an accountable
process to ensure ‘‘meaningful and
timely input by State and local officials
in the development of regulatory
policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’ Under
Executive Order 13132, EPA may not
issue a regulation that has federalism
implications, that imposes substantial
direct compliance costs, and that is not
required by statute, unless the Federal
government provides the funds
necessary to pay the direct compliance
costs incurred by State and local
governments, or EPA consults with
State and local officials early in the
process of developing the proposed
regulation. EPA also may not issue a
regulation that has federalism
implications and that preempts State
law unless the Agency consults with
State and local officials early in the
process of developing the proposed
regulation.
This rule will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132, because it
merely approves and disapproves State
rules implementing a Federal standard,
and does not alter the relationship or
the distribution of power and
responsibilities established in the Clean
Air Act. Thus, the requirements of
section 6 of the Executive Order do not
apply to this rule.
F. Executive Order 13175, Coordination
With Indian Tribal Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ This final rule does not
have tribal implications, as specified in
Executive Order 13175. It will not have
PO 00000
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39389
substantial direct effects on tribal
governments, on the relationship
between the Federal government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal government and Indian tribes.
Thus, Executive Order 13175 does not
apply to this rule.
G. Executive Order 13045, Protection of
Children From Environmental Health
Risks and Safety Risks
EPA interprets Executive Order 13045
(62 FR 19885, April 23, 1997) as
applying only to those regulatory
actions that concern health or safety
risks, such that the analysis required
under section 5–501 of the Executive
Order has the potential to influence the
regulation. This rule is not subject to
Executive Order 13045, because it
approves State rules implementing a
Federal standard.
H. Executive Order 13211, Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not subject to Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001) because it is
not a significant regulatory action under
Executive Order 12866.
I. National Technology Transfer and
Advancement Act
Section 12 of the National Technology
Transfer and Advancement Act
(NTTAA) of 1995 requires Federal
agencies to evaluate existing technical
standards when developing a new
regulation. To comply with NTTAA,
EPA must consider and use ‘‘voluntary
consensus standards’’ (VCS) if available
and applicable when developing
programs and policies unless doing so
would be inconsistent with applicable
law or otherwise impractical.
The EPA believes that VCS are
inapplicable to this action. Today’s
action does not require the public to
perform activities conducive to the use
of VCS.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898, ‘‘Federal
Actions to Address Environmental
Justice in Minority Populations and
Low-Income Populations’’ (February 16,
1994) establishes Federal executive
policy on environmental justice. Its
main provision directs Federal agencies,
to the greatest extent practicable and
permitted by law, to make
environmental justice part of their
E:\FR\FM\08JYR2.SGM
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Federal Register / Vol. 75, No. 130 / Thursday, July 8, 2010 / Rules and Regulations
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies and activities on minority
populations and low-income
populations in the United States. The
Executive Order has informed the
development and implementation of
EPA’s environmental justice program
and policies. Consistent with the
Executive Order and the associated
Presidential Memorandum, the
Agency’s environmental justice policies
promote environmental protection by
focusing attention and Agency efforts on
addressing the types of environmental
harms and risks that are prevalent
among minority, low-income and Tribal
populations.
This action will not have
disproportionately high and adverse
human health or environmental effects
on minority, low-income or Tribal
populations because it increases the
level of environmental protection for all
affected populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population.
Specially, EPA’s simultaneous limited
approval and limited disapproval of
Regulation VIII would have the effect of
strengthening environmental
requirements throughout ICAPCD, and
would not relax environmental
requirements in any area.
K. Congressional Review Act
srobinson on DSKHWCL6B1PROD with RULES2
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
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Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. section 804(2). This
rule will be effective on August 9, 2010.
L. Petitions for Judicial Review
Under section 307(b)(1) of the Clean
Air Act, petitions for judicial review of
this action must be filed in the United
States Court of Appeals for the
appropriate circuit by September 7,
2010. Filing a petition for
reconsideration by the Administrator of
this final rule does not affect the finality
of this rule for the purposes of judicial
review nor does it extend the time
within which a petition for judicial
review may be filed, and shall not
postpone the effectiveness of such rule
or action. This action may not be
challenged later in proceedings to
enforce its requirements (see section
307(b)(2)).
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Particulate matter, Reporting and
recordkeeping requirement.
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Dated: June 15, 2010.
Jared Blumenfeld,
Regional Administrator, Region IX.
Part 52, chapter I, title 40 of the Code
of Federal Regulations is amended as
follows:
■
PART 52—[AMENDED]
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart F—California
2. Section 52.220 is amended by
adding paragraph (c)(345)(i)(E) to read
as follows:
■
§ 52.220
Identification of plan.
*
*
*
*
*
(c) * * *
(345) * * *
(i) * * *
(E) Imperial County Air Pollution
Control District.
(1) Rule 800,‘‘General Requirements
for Control of Fine Particulate Matter
(PM–10),’’ adopted on October 10, 1994,
revised on November 25, 1996 and
revised on November 8, 2005.
(2) Rule 801,‘‘Construction &
Earthmoving Activities,’’ Rule 802,
‘‘Bulk Materials,’’ Rule 803,‘‘Carry-Out &
Track-Out,’’ Rule 804,‘‘Open Areas,’’
Rule 805,’’Paved & Unpaved Roads,‘‘
Rule 806,’’Conservation Management
Practices,’’ adopted on November 8,
2005.
*
*
*
*
*
[FR Doc. 2010–16350 Filed 7–7–10; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 75, Number 130 (Thursday, July 8, 2010)]
[Rules and Regulations]
[Pages 39366-39390]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-16350]
[[Page 39365]]
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Part III
Environmental Protection Agency
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40 CFR Part 52
Revisions to the California State Implementation Plan, Imperial County
Air Pollution Control District; Final Rule
Federal Register / Vol. 75, No. 130 / Thursday, July 8, 2010 / Rules
and Regulations
[[Page 39366]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R09-OAR-2010-0120; FRL-9169-2]
Revisions to the California State Implementation Plan, Imperial
County Air Pollution Control District
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is finalizing a limited approval and limited disapproval
of revisions to the Imperial County Air Pollution Control District
(ICAPCD or the District) portion of the California State Implementation
Plan (SIP) under the Clean Air Act as amended in 1990 (CAA or the Act).
This action was proposed in the Federal Register on February 23, 2010
and concerns local rules that regulate coarse particulate matter
(PM10) emissions from sources of fugitive dust such as
construction sites, unpaved roads, and disturbed soils in open and
agricultural areas in Imperial County.
DATES: Effective Date: This rule is effective on August 9, 2010.
ADDRESSES: EPA has established docket number EPA-R09-OAR-2010-0120 for
this action. The index to the docket is available electronically at
https://www.regulations.gov and in hard copy at EPA Region IX, 75
Hawthorne Street, San Francisco, California. While all documents in the
docket are listed in the index, some information may be publicly
available only at the hard copy location (e.g., copyrighted material),
and some may not be publicly available in either location (e.g., CBI).
To inspect the hard copy materials, please schedule an appointment
during normal business hours with the contact listed in the FOR FURTHER
INFORMATION CONTACT section.
FOR FURTHER INFORMATION CONTACT: Andrew Steckel, EPA Region IX, (415)
947-4115, Steckel.andrew@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, ``we,'' ``us'' and
``our'' refer to EPA.
Table of Contents
I. Summary of Proposed Action
II. Public Comments and EPA Responses
III. EPA Action
IV. Statutory and Executive Order Reviews
I. Summary of Proposed Action
On February 23, 2010 (75 FR 8008), EPA proposed a limited approval
and limited disapproval of the following rules listed in Table 1, known
collectively as Regulation VIII, that were adopted by ICAPCD and
submitted by the California Air Resources Board (ARB) for incorporation
into the California SIP for the Imperial County serious PM10
nonattainment area.
Table 1
------------------------------------------------------------------------
Local agency Rule No. Rule title Adopted Submitted
------------------------------------------------------------------------
ICAPCD.......... 800 General 11/08/05 06/16/06
Requirements
for Control of
Fine
Particulate
Matter.
801 Construction & 11/08/05 06/16/06
Earthmoving
Activities.
802 Bulk Materials. 11/08/05 06/16/06
803 Carry Out & 11/08/05 06/16/06
Track Out.
804 Open Areas..... 11/08/05 06/16/06
805 Paved & Unpaved 11/08/05 06/16/06
Roads.
806 Conservation 11/08/05 06/16/06
Management
Practices.
------------------------------------------------------------------------
We proposed a limited approval because we determined that these
rules improve the SIP and are largely consistent with the relevant CAA
requirements. We simultaneously proposed a limited disapproval because
some provisions of the rules conflict with the CAA section 110(a)
requirement that SIP rules must be enforceable and the requirement in
section 189(b)(1)(B) for implementation of best available control
measures (BACM) in serious PM10 nonattainment areas such as
Imperial County. We discuss these statutory requirements and the
Regulation VIII deficiencies in detail in the proposed rule and in the
Technical Support Document for that proposal (proposal TSD).\1\ In the
proposed rule and proposal TSD we also discuss our determination of
which fugitive dust source categories addressed by Regulation VIII are
significant and consequently require BACM pursuant to EPA guidance.
This determination was based in part on our 2009 decision \2\ to not
concur with the State's request pursuant to EPA's exceptional events
rule \3\ (EER) to exclude certain exceedances of the PM10
National Ambient Air Quality Standard (NAAQS) in Imperial County from
consideration in regulatory actions under the CAA.\4\
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\1\ Our proposed rule and proposal TSD also describe additional
improvements that we recommend for future ICAPCD modifications of
the rules. This final action is not based on those recommendations.
As a result, we do not respond here to all comments we received on
them.
\2\ Letter with enclosure from Laura Yoshii (EPA), to James
Goldstene (ARB), Re: exceptional events requests regarding
exceedances of the PM10 NAAQS in Imperial County, CA,
December 22, 2009.
\3\ 40 CFR 50.1(j) and 50.14.
\4\ Issues related to the Regulation VIII deficiencies,
significant source categories and our decision not to concur with
the State's exceptional events requests are addressed further below
in our responses to comments we received on the proposed rule.
---------------------------------------------------------------------------
We summarize the Regulation VIII deficiencies addressed in our
proposed rule below. These deficiencies concern Regulation VIII
provisions relating to open areas, unpaved roads and agricultural
lands.
A. BACM-Related Deficiencies for Open Areas
1. Recreational Off-Highway Vehicle Activity
While recreational off-highway vehicle (OHV) \5\ activity causes
much of the PM10 emissions from open areas in Imperial
County, Rule 804 regulates only a small portion of these emissions,
including those from OHV activity on State lands on which the rule is
not being implemented. The vast majority of the OHV emissions in
Imperial County are addressed only by requirements in Rule 800 section
F.5 for dust control plans (DCPs) for sources under the control of the
Bureau of Land Management (BLM). While BLM is required to describe in
the DCPs the dust control measures that it intends to implement, BLM is
not required to implement any specific BACM-level controls for OHV use.
Moreover, ICAPCD has not provided an analysis of BACM for OHV activity,
including
[[Page 39367]]
potential OHV activity in open areas and on unpaved roads and paths
that are exempt from the specific requirements and measures in Rules
804 and 805. The proposed rule and proposal TSD address how ICAPCD can
correct these deficiencies.\6\
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\5\ As used here and in the proposal TSD, the term ``off-highway
vehicle'' or OHV includes all vehicles subject to the exemption in
Rule 800 section E.6 for recreational use of public lands in
Imperial County.
\6\ 75 FR 8008, 8010-8011 and our proposal TSD, section III.B.1.
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2. Definition of ``Disturbed Surface''
The term ``disturbed surface area'' is used in several Regulation
VIII rules but is never defined. For example, Rule 804 applies to a
source category for which BACM is required and relies on the undefined
term to describe rule applicability in Rule 804 section B. A definition
of this term is necessary in order to ensure that these rules are
enforceable at a BACM level.
B. BACM-Related Deficiencies for Unpaved Roads
1. Unpaved Non-Farm Roads
While CAA section 189(b)(1)(B) requires ICAPCD to implement BACM by
2008 (i.e., four years after reclassification to serious),\7\ Rule 805
section E.7 allows the County until 2015 to stabilize heavily-travelled
unpaved roads. This schedule is inconsistent with the statutory
requirement and ICAPCD has not provided adequate evidence that this
schedule is as expeditious as practicable, based upon economic
feasibility or any other appropriate consideration. In addition, Rule
805 section E.7's requirement to stabilize all non-exempt unpaved
County roads is not adequately enforceable as currently structured
because it is not clear that the County is required to implement (and
not just submit) a stabilization plan; stabilize different unpaved
roads each year; and maintain all stabilized roads. The proposed rule
and proposal TSD address how ICAPCD can correct these deficiencies.\8\
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\7\ On August 11, 2004, EPA reclassified Imperial County as
serious nonattainment for PM10. 69 FR 48835. Since 2008
has passed, BACM is now required to be implemented as expeditiously
as practicable. Delaney v. EPA, 898 F.2d 687 (9th Cir. 1990).
\8\ 75 FR 8008, 8011 and our proposal TSD, section III.B.3.
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2. Unpaved Farm Roads and Traffic Areas
Rule 805 section D.2 exempts agricultural roads and traffic areas
from the opacity and stabilization requirements applicable to non-
agricultural operation sites. Farm roads and traffic areas are only
required to implement a conservation management practice (CMP) from the
menus for unpaved roads and traffic areas in Rule 806 in contrast to
analogous rules in other geographical areas.
Rule 806 sections E.3 and E.4 list CMPs intended to control
emissions from agricultural unpaved roads and traffic areas but these
measures are broadly defined and there is no other mechanism in the
rule to ensure specificity. The absence of sufficiently defined
requirements makes it difficult for regulated parties to understand and
comply with the requirements, and makes it difficult for ICAPCD or
others to verify compliance and to enforce the requirements if
necessary. The lack of specificity similarly renders it difficult to
assess whether the measures constitute BACM level controls. The
proposed rule and proposal TSD address how ICAPCD can correct these
deficiencies.\9\
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\9\ 75 FR 8008, 8011 and our proposal TSD, section III.B.4.
---------------------------------------------------------------------------
3. Border Patrol Roads
Rule 800 section F.6.c exempts roads owned or operated by the U.S.
Border Patrol (BP) from Rule 805 requirements that are ``inconsistent
with BP authority and/or mission.'' It is not clear what this exemption
is intended to address, or how it would be implemented and enforced in
order to meet BACM requirements. The proposed rule addresses how ICAPCD
can correct these deficiencies.\10\
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\10\ 75 FR 8008, 8011.
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C. BACM-Related Deficiencies for Agricultural Lands
1. Tilling and Harvesting
Rule 806 sections E.1 and E.2 list CMPs intended to control
emissions from agricultural land preparation and cultivation (including
tilling), and harvest activities, but these measures are broadly
defined and there is no other mechanism in the rule to ensure
specificity. The absence of sufficiently defined requirements makes it
difficult for regulated parties to understand and comply with the
requirements, and makes it difficult for ICAPCD or others to verify
compliance and to enforce the requirements if necessary. The lack of
specificity similarly renders it difficult to assess whether the
measures constitute BACM level controls.
In addition, Rule 806 section E requires one CMP from the ``land
preparation and cultivation'' category and one CMP from the
``harvesting'' category, while rules in other geographic areas have
more stringent requirements.
The proposed rule and proposal TSD address how ICAPCD can correct
these deficiencies.\11\
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\11\ 75 FR 8008, 8011-8012 and our proposal TSD, section
III.B.4.
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2. Windblown Dust
Windblown dust from non-pasture agricultural lands is also a
significant source of PM10 that requires BACM independent of
agricultural tilling. The CMPs in Rule 806 section E, however, mainly
control emissions by reducing the number of vehicle passes across
fields, and sources are not required to select BACM level practices for
controlling windblown dust from active or fallow agricultural fields.
The proposed rule and proposal TSD address how ICAPCD can correct these
deficiencies.\12\
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\12\ 75 FR 8008, 8012 and our proposal TSD, section III.B.4.
---------------------------------------------------------------------------
D. Non-BACM Deficiency
Rule 802 section D.1 allows the Air Pollution Control Officer
(APCO) to set aside controls that might be used instead of water to
stabilize surfaces of bulk materials. This discretion allows ICAPCD to
approve alternatives to the applicable SIP without following the SIP
revision process described in CAA section 110. Moreover, ICAPCD has not
demonstrated why such discretion is needed for measures such as
covering, enclosing or sheltering material piles. The proposed rule
addresses how ICAPCD can correct these deficiencies.\13\
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\13\ 75 FR 8008, 8012.
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II. Public Comments and EPA Responses
EPA's proposed action provided a 30-day public comment period.
During this period, we received nine unique comment letters from public
agencies and broad-based organizations.
Brad Poiriez, Air Pollution Control Officer, Imperial
County Air Pollution Control District, March 25, 2010 (ICAPCD).
Daniel Steward, Acting Field Manager, United States
Department of the Interior, Bureau of Land Management, El Centro
Resource Area, March 24, 2010 (BLM).
Kathleen Dolinar, District Superintendent, Ocotillo Wells
District, California State Parks, Off-Highway Motor Vehicle Recreation
Division, by e-mail dated March 24, 2010 (OWD).
Gail Sevrens, Acting District Superintendent, Colorado
Desert District, California State Parks, by e-mail dated March 25, 2010
(CDD).
David P. Hubbard, Gatzke Dillon & Balance LLP, on behalf
of EcoLogic
[[Page 39368]]
Partners, Inc., March 25, 2010 (EcoLogic).
Lisa T. Belenky, Senior Attorney, Center for Biological
Diversity, March 25, 2010, representing several listed parties (CBD).
Jose Luis Olmedo, Executive Director, Comite Civico Del
Valle, Inc., March 25, 2010, submitted and joined by other parties
(Comite).
Ayron Moiola, Executive Director, Coalition of Labor,
Agriculture & Business, March 24, 2010 (COLAB).
Mark McBroom, President, Imperial County Farm Bureau,
March 24, 2010 (Farm Bureau).
We also received over 100 comment letters from individuals and
organizations associated with recreational OHV activities. We reference
these comments below by their identification in the Federal docket
management system (FDMS) found at regulations.gov. For example, the
comment listed in FDMS as document number ``EPA-R09-OAR-2010-0120-
0219'' is referenced below as ``0219.''
We summarize the comments and provide our responses below. In our
responses we identify specific commenters in some cases but not in
others, particularly where many commenters made similar points.
A. General
These overarching comments largely provide general support or
opposition to our proposal.
General #1: CBD and Comite support EPA's proposal to find that the
Regulation VIII submittal does not fully implement BACM level controls
for all significant source categories in Imperial County, and support
EPA's nonconcurrence with associated exceptional event requests. They
ask EPA to finalize the proposed limited disapproval of Regulation VIII
and to require additional PM10 emissions restrictions. Many
other commenters disagree with EPA's proposed limited disapproval,
especially with EPA's identification of deficiencies for BACM
requirements and EPA's nonconcurrence with exceptional events. ICAPCD,
for example, believes that EPA's proposal is arbitrary and capricious,
and that California has demonstrated that all required BACM are being
implemented in Imperial County.
Response: No response is necessary for the overarching statements
of support or opposition. Responses are provided below to the specific
comments that support these general statements.
General #2: Several commenters believe that EPA's proposal lacks
adequate scientific support. One (0144), for example, states that
passing sweeping air quality regulations in an area with unique terrain
and climate with only generalities to prove the sources of pollution is
unethical and appears anti-development, anti-OHV and anti-agriculture.
Response: The scientific support for EPA's action is documented in
our proposal and the associated proposal TSD and discussed further in
response to specific comments below. See, for example, response to
comment EI 3 below. The serious health impacts of exposure to
elevated levels of PM10 are well known and well documented
and need not be reiterated here.
General #3: ICAPCD objects to EPA taking over four years to act on
its submittals of Regulation VIII for approval and claims that EPA is
only now raising basic issues that ICAPCD believes should have been
resolved before rule adoption. For example, ICAPCD objects to EPA
disapproving a definition that it claims is clear and understood by all
affected parties. ICAPCD and others (e.g., COLAB) comment that EPA
never raised this and other concerns despite ICAPCD's extensive public
process and communication with EPA before rule adoption. ICAPCD also
cites EPA's testimony before the District Board in which the Agency
supported Regulation VIII as BACM. As a result, ICAPCD concludes that
EPA's proposal undermines ICAPCD's ability to rely on EPA comments in
the future.
Response: EPA reviews and comments on many draft State and local
agency rules during their development prior to submittal to EPA for
formal approval. It is generally more efficient for all parties to
identify and resolve issues early in the process, rather than after
rules are adopted and submitted to EPA for inclusion into the SIP.
EPA's formal action on local rules, however, can only occur through
notice and comment rulemaking after rules have been officially
submitted to EPA by the State. If EPA determines during that process
that a submittal does not fulfill relevant CAA requirements, we cannot
approve the submittal. Given time and resource constraints, it is not
always possible for the Agency to identify or analyze fully all issues
before State or local rule adoption. Moreover, EPA must carefully
consider all public comments submitted on proposed EPA actions on State
and local rules. Such comments often identify issues and concerns that
may not have arisen during the prior evaluation of drafts of a rule. We
continue to believe, however, that communication between EPA and State
and local agencies at the rule development stage is productive.
General #4: OWD asks EPA to extend the comment period because it
was informed of EPA's proposal only nine days before the close of the
comment period. Several commenters also state that EPA did not provide
adequate notification time (0218.1 and 0098) or consultation with State
Park personnel (0218.1 and OWD).
Response: EPA denied OWD's request to extend the comment period
because EPA is under a court order \14\ to finalize action by June 15,
2010, and needs time to analyze all comments submitted on the
proposal.\15\ While more time and outreach before EPA action is always
desirable, nothing in the comments suggests that EPA failed to follow
relevant public notification requirements found in the Administrative
Procedures Act.\16\ EPA notes that OWD did comment on the proposal and
EPA has taken those comments into consideration in the final action.
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\14\ Comite Civico Del Valle, Inc., v. Jackson, No. 09-cv-04095
PJH (N.D. Cal.).
\15\ E-mail from Andrew Steckel, EPA, to Kathleen Dolinar,
California State Parks, March 29, 2010.
\16\ See 5 U.S.C. 553.
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B. State Implementation Plan (SIP)
These comments generally address broad SIP issues rather than
specific Regulation VIII provisions.
SIP #1: OWD believes the PM10 standard is nearly
impossible to attain given Imperial's climate, natural desert
condition, the cost of inappropriate BACM, and other local conditions.
In contrast, Comite asks EPA to find that California has failed to
submit a PM10 plan as required by 72 FR 70222 (December 11,
2007), and to consider imposing associated CAA section 179 sanctions
and a section 110(c) Federal implementation plan (FIP) in this area.
Response: Our proposed action addresses the CAA section
189(b)(1)(B) requirement for BACM for certain PM10 sources
in Imperial County. The submittal at issue, Regulation VIII, is but one
portion of the complete SIP that ICAPCD must develop in order to meet
additional CAA requirements. These comments address the separate and
broader statutory obligations for the State to submit a PM10
plan that, among other things, demonstrates expeditious attainment of
the PM10 NAAQS. Those other obligations are not the subject
of this action.
SIP #2: ICAPCD does not believe that any additional controls such
as those that may need to be implemented if EPA partially disapproves
Regulation VIII
[[Page 39369]]
will prevent PM10 exceedances during high winds or otherwise
materially benefit air quality on days unaffected by high winds. ICAPCD
further believes that such additional controls will waste limited
resources that should be used in other ways to improve local air
quality in the area.
Response: CAA section 189(b)(1)(B) and EPA guidance \17\ require
that BACM be implemented for all significant source categories \18\ in
serious PM10 nonattainment areas such as Imperial County. As
explained in our proposal,\19\ we determined that each of the
subcategories under open areas, unpaved roads and agricultural lands
below meet or exceed the 5 [micro]g/m\3\ de minimis level in our
guidance and are therefore significant source categories in Imperial
County:
---------------------------------------------------------------------------
\17\ ``State Implementation Plans for Serious PM-10
Nonattainment Areas, and Attainment Date Waivers for PM-10
Nonattainment Areas Generally; Addendum to the General Preamble for
the Implementation of Title I of the Clean Air Act Amendments of
1990;'' 59 FR 41998 (August 16, 1994) (General Preamble Addendum).
\18\ Under the General Preamble Addendum, a source category
``will be presumed to contribute significantly to a violation of the
24-hour NAAQS if its PM10 impact at the location of the
expected violation would exceed 5 [micro]g/m\3\.'' This is also
referred to as the de minimis level. Id. at 42011.
\19\ 75 FR 8008, 8010, and proposal TSD, pp. 5-7.
---------------------------------------------------------------------------
Open areas:
--Windblown Dust, Other Open Area.
Unpaved roads:
--Entrained Unpaved Road Dust, City/County.
--Entrained Unpaved Road Dust, Canal.
--Windblown Dust, Unpaved City/County Road.
--Windblown Dust, Unpaved Canal Road.
--Windblown Dust, Unpaved Farm Road.
Agricultural lands:
--Tilling.
--Windblown Dust, Non-Pasture Agricultural Lands.
As EPA stated in the guidance, the structural scheme throughout
title I of the CAA, including its provisions for the PM10
NAAQS, requires the implementation of increasingly stringent control
measures in areas with more serious pollution problems. EPA further
stated ``that the more serious the air quality problem, the more
reasonable it is to require States to implement control measures of
greater stringency despite the greater burdens such measures are likely
to cause.'' \20\ Imperial County continues to violate the
PM10 standard \21\ and our proposed action identifies
several components of the State's Regulation VIII submittal relating to
open areas, agricultural lands and unpaved roads that do not fulfill
the CAA BACM requirement and the enforceability requirements of CAA
section 110(a).
---------------------------------------------------------------------------
\20\ General Preamble Addendum at 42010.
\21\ EPA's Air Quality System Preliminary Design Value Report
(May 18, 2010) shows 17 exceedances of the 24-hour PM10
NAAQS in Imperial County between 2007 and 2009.
---------------------------------------------------------------------------
We further address ICAPCD's contention that additional Regulation
VIII controls will not prevent PM10 exceedances during high
winds in our response to comment EE 1 below.
SIP #3: Many commenters emphasize the importance of OHV areas in
Imperial County for recreation, and believe that enjoyment of the
desert should not be restricted. Commenters note that many
organizations help keep the desert clean, and one commenter (0175.1)
believes such efforts would be reduced if OHV areas are closed.
Response: Recreation, enjoyment of the desert and clean deserts are
certainly desirable, whether for OHV use or otherwise. However, except
as implicit in our response to comment OHV 5 below, they are
not germane to the evaluation in our proposal and in this final rule of
Regulation VIII and its compliance with the applicable CAA
requirements.
SIP #4: Two commenters (OWD and 0218.1) question whether EPA's
proposal is based on statistically significant data since there were
only three PM10 exceedances within a three year period.
Response: ICAPCD's obligation to implement BACM for Regulation VIII
fugitive dust sources derives from the Imperial County's designation as
nonattainment and classification as serious. On November 15, 1990, the
date of enactment of the 1990 Clean Air Act Amendments, Imperial County
was designated nonattainment and classified as moderate.\22\ On August
11, 2004, EPA reclassified the area as serious in compliance with a
mandate of the U.S. Court of Appeals for the Ninth Circuit.\23\ The
reclassification, pursuant to CAA section 188(b)(2), was based on a
finding that the area failed to attain the PM10 NAAQS by the
statutory deadline of December 31, 1994. Once reclassified to serious,
the area was required to comply with CAA section 189(b)(1)(B), which
required that BACM be implemented for the area four years after its
reclassification to serious.
---------------------------------------------------------------------------
\22\ 56 FR 56694 (November 6, 1991).
\23\ 69 FR 48792; Sierra Club v. United States Environmental
Protection Agency, et al., 346 F.3d 995 (9th Cir. 2003); cert.
denied, 542 U.S. 919 (2004).
---------------------------------------------------------------------------
The three exceedances to which OWD refers occurred during 2006 and
2007. The State requested that these exceedances be excluded from use
in regulatory actions pursuant to EPA's EER.\24\ Because we did not
concur with the State's request, BACM is required to be implemented for
certain windblown dust source categories, including open areas, for
which such controls would not have been required if we had agreed with
the State.\25\ See our responses to Exceptional Events comments below.
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\24\ See section II.D.1 below.
\25\ 75 FR 8008, 8010 and proposal TSD pp. 5-7.
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We also note that California has chosen to sample PM10
in Imperial County only one out of every six days. As a result, by
regulation, each monitored exceedance is estimated to represent
approximately six exceedances rather than one.\26\ For example, in
2009, ICAPCD reported three monitored exceedances at the Ethel Street
monitoring site, which are estimated to represent 18.3 exceedances.
Exceedances were also monitored at Brawley, El Centro, Westmorland and
Niland in 2009.\27\
---------------------------------------------------------------------------
\26\ 40 CFR part 50, appendix K.
\27\ EPA's Air Quality System Preliminary Design Value Report
(May 18, 2010).
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SIP #5: Comite believes PM10 should be further
controlled in Imperial County by adoption of local fugitive dust
ordinances like those in Coachella's Cathedral City, and by
strengthening open burning regulations to be similar to those in the
South Coast Air Quality Management District (SCAQMD) and the San
Joaquin Valley Unified Air Pollution Control District (SJVUAPCD).
Response: We assume the commenter refers to title 8, chapter 8.54
of Cathedral City's municipal code which describes requirements for
construction, unpaved roads and other local dust sources.\28\ These
requirements are generally similar to the type of controls adopted by
SCAQMD (e.g., Rule 403), SJVUAPCD (e.g., Regulation VIII) and ICAPCD
(Regulation VIII). The commenter does not identify any specific
Cathedral City controls that it believes are needed in ICAPCD
Regulation VIII to constitute BACM. Except where identified in our
proposal, we believe ICAPCD's BACM analyses include adequate evaluation
of analogous fugitive dust controls in other areas.\29\ It is possible
that the commenter is recommending duplicative city ordinances that
overlap County-wide Regulation VIII. While such redundancy could
improve compliance, it is generally not necessary
[[Page 39370]]
to meet CAA section 110(a) enforceability requirements.
---------------------------------------------------------------------------
\28\ Cathedral City Municipal Code, title 8, chapter 8.54,
Fugitive Dust Control; https://qcode.us/codes/cathedralcity/.
\29\ 2009 PM10 SIP table 4.2 and 2005 BACM analysis
table 4.2.
---------------------------------------------------------------------------
Finally, our proposed action only addresses the ICAPCD controls for
certain PM10 source categories encompassed by Regulation
VIII, and therefore does not address control of open burning or many
other air pollution sources in Imperial County. See also responses to
comments SIP 1 and EI 1.
SIP #6: Comite cites Vigil v. Leavitt, 381 F.3d 826, 834 (9th Cir.
2004) and Hall v. EPA, 273 F.3d 1146 (9th Cir. 2001), in commenting
that measures in other areas can be considered BACM for Imperial County
and are per se feasible. Comite further argues that what constitutes
BACM can strengthen over time. In contrast, OWD does not believe that
Imperial County should apply mitigation measures from other geographic
areas (e.g., SJVUAPCD and Maricopa) that have different geologic and
other local conditions. Similarly, COLAB believes that different
cultural practices prevent ICAPCD from blindly implementing controls
imposed in other areas, although the ICAPCD and SJVUAPCD CMP rules are
very similar. Still another commenter (0119) claims that similar
restrictions on construction, OHVs, farmers, etc., in Las Vegas and
elsewhere have not been effective, and there is no need for such
draconian and ineffective bureaucratic rules.
Response: EPA believes that it is appropriate, when evaluating what
constitutes BACM for a given source category, to consider controls that
have been adopted and implemented in other geographical areas. EPA
agrees that the facts and circumstances in a given area can affect what
constitute BACM for that area, but that this determination must be
based upon appropriate consideration of relevant information specific
to that area.
Comite does not explain how the cited cases support its position.
Nonetheless, we agree that in evaluating BACM for Imperial County,
ICAPCD should analyze analogous measures in other areas and that BACM
may strengthen over time.\30\ Our proposal identifies several
significant deficiencies in ICAPCD's analysis to date.\31\ While BACM
is determined on a case-by-case basis \32\ and, as such, the analysis
can include evaluation of local conditions that might make specific
controls economically and/or technologically feasible in one area but
not another,\33\ neither the 2009 PM10 SIP \34\ nor the
comment provides sufficient detail to adequately address the
deficiencies identified in our proposal.
---------------------------------------------------------------------------
\30\ General Preamble Addendum at 42013-42014.
\31\ E.g., OHV controls in Arizona Revised Statute Sec. 49-
457.03 and Clark County Air Quality Regulations, section 90 (75 FR
8011, February 23, 2010).
\32\ General Preamble Addendum at 42010 and 42012.
\33\ In this respect, we do not agree with Comite that measures
adopted in other areas are automatically transferable to Imperial
County.
\34\ ``2009 Imperial County State Implementation Plan for
Particulate Matter Less Than 10 Microns in Aerodynamic Diameter,
Final,'' adopted by ICAPCD Governing Board on August 11, 2009. (2009
PM10 SIP).
---------------------------------------------------------------------------
OWD does not explain how Imperial County differs so markedly from
the San Joaquin Valley and the Maricopa area that it would be
inappropriate to consider BACM approved in those areas as part of the
evaluation of controls for the same source categories in Imperial
County. Similarly, COLAB does not elaborate on what ``cultural
practices'' in Imperial County would justify disregarding approved BACM
in the San Joaquin Valley and the Maricopa area as part of the
evaluation of what controls would be appropriate for comparable source
categories in Imperial County.
C. Emissions Inventory (EI)
EI #1: Many commenters oppose further OHV controls because they
believe OHVs contribute little to Imperial County's PM10
pollution problem compared to other sources. Commenters identify
various sources they believe are more significant and/or should be
further addressed instead, including fallow fields, fireplaces, feed
lots, agricultural burning, pesticides, dirt roads, inefficient street
lights, insufficient public transportation, insufficient speed limit
enforcement, Interstate 8, the New River, the Salton Sea, Arizona to
the east, San Diego to the west, Mexican roads, fires and factories to
the south, rain, wind, erosion, dust storms and other natural
occurrences. These commenters include OWD, 0096, 0097, 0150, 0139,
0152, 0180, 0192, 0194 and 0219.1.
Response: Our proposal explains that BACM is required for all
significant PM10 source categories in Imperial County, that
windblown dust from open areas is a significant PM10 source
category, and that OHVs greatly increase emissions from open areas in
Imperial County.\35\ Our proposal further explains that ICAPCD has not
demonstrated implementation of BACM for open areas with respect to
OHVs.\36\ These conclusions are based on inventory information prepared
by ICAPCD and ARB and used during development of Regulation VIII and
the 2009 PM10 SIP.\37\
---------------------------------------------------------------------------
\35\ Proposal TSD, pp. 5-8.
\36\ Id. at p. 8.
\37\ Id. at pp. 5-8.
---------------------------------------------------------------------------
The inventory in the 2009 PM10 SIP represents the most
comprehensive information currently available on OHV emissions in
Imperial County.\38\ ICAPCD's analysis in the 2009 PM10 SIP
concluded that windblown dust from open areas was not a significant
source category, but this conclusion was premised upon many exceedences
of the NAAQS being deemed to be the result of exceptional events.
However, EPA's own conclusion regarding those exceedences is that they
were not caused by exceptional events and, as a result, we consider
windblown dust from open areas to be a significant source category that
is subject to the CAA's BACM requirement. See response to comment SIP
4 and responses to Exceptional Events comments in section II.D
below. Therefore ICAPCD has failed to meet the BACM requirement for
windblown dust from open areas, in part because ICAPCD has not
evaluated what controls might be appropriate for OHV activities in such
areas.
---------------------------------------------------------------------------
\38\ 2009 PM10 SIP, Chapter 3; Appendix III.
---------------------------------------------------------------------------
EPA's action on the Regulation VIII submittal does not address or
depend on whether additional controls may also be appropriate for the
various other sources identified in the comments.
EI #2: One commenter (0188) had driven past many farms in El Centro
during tilling and observes that the dust was very minimal. Another
(0201) thinks more attention should be paid to agriculture which the
commenter believes is exempt from many of the environmental
regulations.
Response: See response to comment EI 1. Similar to
emissions from open areas, EPA has concluded that emissions associated
with tilling on and windblown dust from agricultural lands are
significant source categories in Imperial County and, as such, ICAPCD
needs to meet the BACM requirement for such sources.\39\
---------------------------------------------------------------------------
\39\ Proposal TSD, pp. 5-8 and 9-11.
---------------------------------------------------------------------------
The commenter (0201) concerned about exemptions for agriculture did
not specify which regulations exempt agriculture. As explained in our
proposal, however, because certain agricultural-related activities
constitute a significant source category for PM10 in
Imperial County, ICAPCD is required to meet the CAA's BACM requirements
for such sources. Any ``exemptions'' for any such sources would need to
be justified and explained in the context of meeting the BACM
requirements.
EI #3: Several commenters claim that EPA has not proved the impact
of OHVs
[[Page 39371]]
on PM10 levels sufficient to require additional OHV
regulations. OWD notes, for example, that: (1) EPA did not analyze
extreme terrain, thermal stability and other effects on winds in the
desert; (2) most emissions from open lands come from undisturbed shrub/
grassland which are not anthropogenic sources; and (3) ICAPCD's 2009
PM10 SIP, on which EPA relies, uses worst-case assumptions
rather than actual soil condition information to estimate that OHVs
represent less than 5% of the County's total PM10 emissions
(13.9 of 282 tpd). OWD states that 99% of these total emissions relate
to OHVs subject to Federal and State stewardship. Therefore OWD
concludes that actual OHV emissions are small compared to worst-case
estimates. OWD also questions EPA's reference for the estimate of 22
tpd of windblown PM10 from OHVs.
EcoLogic believes that EPA needs monitoring in the Ocotillo Wells
State Vehicle Recreation Area (SVRA) and other areas to show how
specific OHV activity affects sensitive receptors and for EPA to
identify OHV activity as a major contributor to the County's
PM10 problem. Another commenter believes EPA lacks data
tying PM to specific OHV activities (0218.1), and several commenters
believe that any pollution from OHVs is virtually immeasurable. Several
commenters believe additional inventory analysis is particularly
important because OHV areas are far from population centers and
monitors with PM10 exceedances. One commenter (0131)
requests an unbiased third-party study of OHV impacts. CDD explains
that PM10 emissions from several specific parks in Imperial
County should be low, partly because OHV activity is prohibited. In
contrast, CBD supports EPA's claim that OHVs on BLM land cause
considerable PM10 in Imperial County, and notes that BLM
previously estimated PM10 impacts from OHV activities at the
Aldodones Dunes alone as high as 11 tpd on holiday weekends.
Response: It is extremely difficult to quantify and speciate
accurately the myriad sources of PM10 emissions and
PM10 precursor emissions spatially and temporally for
purposes of modeling air pollution impacts and developing cost
effective control programs. As a result, emission inventories are
constantly being refined as more and better science and data become
available. However, EPA, State and local air pollution agencies must
make policy and regulatory decisions based on the best information
available to comply with the CAA. As discussed in response to comment
EI 1, the inventory and other information underlying our
proposal regarding the emissions from OHV activity and the impacts of
such activity represent the most comprehensive information currently
available.
Regarding specific concerns in this comment:
(1) EPA's conclusion that BACM is required for OHV activity relies
on emissions inventory estimates that ICAPCD developed. If appropriate,
ICAPCD could choose to refine those estimates to take into
consideration factors such as terrain, thermal stability and other
effects on winds in the desert, as well as distances between OHV areas
and population centers and additional third party analysis. Such
refinements are beyond the level of detail normally used in inventories
required by CAA section 172(c)(3).\40\
---------------------------------------------------------------------------
\40\ See, e.g., AP-42, Fifth Edition, Volume I, Chapter 13:
Miscellaneous Sources, 13.2.2--Unpaved Roads, Final Section, EPA,
November 2006. This document provides EPA guidance on estimating
emissions on unpaved roads and does not, for example, account for
road terrain. https://www.epa.gov/ttn/chief/ap42/ch13/.
---------------------------------------------------------------------------
(2) ICAPCD in its 2009 PM10 SIP quantifies the impact of
soil type and land cover (e.g., shrub/grassland) and degree of OHV
disturbance in OHV emission estimates relied on by our proposal.\41\
---------------------------------------------------------------------------
\41\ 2009 PM10 SIP, appendix III.B.
---------------------------------------------------------------------------
(3) ICAPCD used the best available information regarding soil types
in open areas and determined that the remaining uncertainty does not
affect the results of the technical analyses.\42\
---------------------------------------------------------------------------
\42\ 2009 PM10 SIP, p. 3-2.
---------------------------------------------------------------------------
(4) Even OWD's 13.9 tpd OHV emission estimate, which we believe is
too low,\43\ exceeds the presumptive 5 [micro]g/m\3\ de minimis level
for source categories requiring BACM.\44\
---------------------------------------------------------------------------
\43\ In comparison to ICAPCD's 22 tpd estimate. Proposal TSD,
footnote 32.
\44\ As discussed on pp. 5-8 of the proposal TSD, depending on
the specific monitor, 2-3% of Imperial County's annual inventory is
calculated to result in a 5 [micro]g/m\3\ contribution, which
equates to about 6-8 tpd emissions.
---------------------------------------------------------------------------
(5) The reference for 22 tpd of windblown OHV emissions is
accurately explained in our proposal.\45\
---------------------------------------------------------------------------
\45\ Id.
---------------------------------------------------------------------------
The comment that monitoring is necessary in the Ocotillo Wells SVRA
and other areas before EPA should require controls for OHV activities
is incorrect. As stated previously, under CAA section 189(b) and EPA
guidance, BACM is required for all significant source categories in the
nonattainment area, including windblown dust in open areas caused by
OHV activity.\46\ Thus monitoring, which could provide valuable
information, is nevertheless not necessary to determine which source
categories require BACM.
---------------------------------------------------------------------------
\46\ See, e.g., proposal TSD, p. 5.
---------------------------------------------------------------------------
D. Exceptional Events (EE)
1. Background
On March 22, 2007, EPA adopted a final rule to govern the review
and handling of certain air quality monitoring data for which the
normal planning and regulatory processes are not appropriate.\47\ Under
the rule, EPA may exclude data from use in determinations of NAAQS
exceedances and violations if a State demonstrates that an
``exceptional event'' caused the exceedances. Before EPA can exclude
data from these regulatory determinations, the State must flag the data
in EPA's Air Quality System database and, after notice and opportunity
for public comment, submit a demonstration to EPA to justify the
exclusion. After considering the weight of evidence provided in the
demonstration, EPA decides whether or not to concur with each flag.
---------------------------------------------------------------------------
\47\ ``Treatment of Data Influenced by Exceptional Events,'' 72
FR 13560 (March 22, 2007) (EER).
---------------------------------------------------------------------------
On May 21, 2009, ARB submitted demonstrations for ``high wind''
events that allegedly caused ten exceedances of the 24-hour
PM10 standard at various monitors in Imperial County in 2006
and 2007. The demonstrations consisted of the following support
documents (listed in Table 2) prepared by ARB, ICAPCD, and ICAPCD's
contractor, ENVIRON:
Table 2
----------------------------------------------------------------------------------------------------------------
Description Document date Abbreviated title
----------------------------------------------------------------------------------------------------------------
Natural Event Documentation: Calexico and January 30, 2009........ September NED.\48\
Westmorland, California--September 2, 2006.
Natural Event Documentation: Brawley and April 15, 2008.......... Original April NED.
Westmorland, California--April 12, 2007
[enclosed with June 13, 2008 letter to Sean
Hogan].
[[Page 39372]]
Natural Event Documentation: Brawley, Calexico, April 15, 2008.......... Original June NED.
El Centro, Niland, and Westmorland, California--
June 5, 2007, Imperial County Air Pollution
Control District [enclosed with June 13, 2008
letter to Sean Hogan].
Natural Event Documentation: Brawley and March 12, 2009.......... April NED.
Westmorland, California--April 12, 2007
[addendum to June 13, 2008 submittal].
Natural Event Documentation: Imperial County, March 12, 2009.......... June NED.
California--June 5, 2007 [addendum to June 13,
2008 submittal].
----------------------------------------------------------------------------------------------------------------
As stated above in section I, on December 22, 2009, EPA denied
ARB's request to exclude all of the exceedances as exceptional events.
The basis for our decision is specified in an enclosure which
accompanied the December 22, 2009 letter.\49\ By letter, including
Attachment A and Appendix A1, dated March 3, 2010, ICAPCD asked EPA to
reconsider this decision.\50\
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\48\ We refer to the natural event documentation in these five
documents, collectively, as the NEDs.
\49\ See footnote 2. We refer to our December 22, 2009 letter
and the enclosure hereafter as ``2009 EE decision.''
\50\ Letter from Brad Poiriez (ICAPCD) to Jared Blumenfeld
(EPA), March 3, 2010 with Attachment A and Appendix A1.
---------------------------------------------------------------------------
Our proposal on Regulation VIII explained that our 2009 EE decision
led to an adjustment of ICAPCD's significant source analysis which in
turn led us to modify the list of significant sources for which BACM
must be implemented in Imperial County under CAA section
189(b)(1)(B).\51\ As a result, our 2009 EE decision was the subject of
public comments on our proposed action. ICAPCD resubmitted its March 3,
2010 letter, including Attachment A and Appendix A1, regarding our 2009
EE decision as Appendix C to its March 25, 2010 comment letter on our
Regulation VIII proposed action.\52\ EPA also received comments
pertaining to our exceptional events decision from Comite and CBD. A
summary of these comments and our responses follow.
---------------------------------------------------------------------------
\51\ See 75 FR 8010 and the proposal TSD, pp. 5-7.
\52\ We refer to ICAPCD's March 10, 2010 letter with its
Attachment A and Appendix A1, collectively, throughout our responses
to the exceptional events comments in section II.D as
``Attachment.''
---------------------------------------------------------------------------
2. Events Not Reasonably Controllable or Preventable
EE #1: ICAPCD (Attachment) disagrees with EPA's interpretation of
the requirement in the EER at 40 CFR 50.1(j) that in order for an event
to meet the regulatory definition of exceptional event, such event must
be ``not reasonably controllable or preventable.'' Specifically ICAPCD
takes issue with EPA's statement in our 2009 EE decision that this
criterion inherently implies ``a requirement that the State demonstrate
that anthropogenic sources contributing to the exceedance caused by the
event were reasonably well controlled.'' ICAPCD believes that under the
plain regulatory language it is irrelevant whether ``reasonable and
appropriate'' controls are in place on the day of an otherwise
qualifying event when it can be shown that such controls would not
reduce emissions and impact at the monitor sufficiently to prevent the
exceedance. ICAPCD believes that it is inconsistent with the intent of
the CAA for EPA to refuse to concur with an exceptional event claim
solely due to EPA's dissatisfaction with the stringency of certain
controls when such controls could not have prevented the exceedance.
Response: ICAPCD mischaracterizes both the plain language and the
regulatory intent of 40 CFR 50.1(j) by reading the words ``reasonably
controllable or'' out of that section. The regulation clearly requires
a showing that the event is not either reasonably controllable or
preventable, not as ICAPCD would have it, that the event cannot be
controlled to the extent that no exceedance would have occurred.
Furthermore, ``control'' as generally used in the CAA and EPA guidance
(e.g., RACT and BACM \53\), and as defined in the dictionary means to
regulate or to reduce the incidence or severity.\54\ Thus the meaning
of the word ``control'' undeniably differs from the words ``eliminate''
or ``prevent.'' Therefore, to meet the ``not reasonably controllable or
preventable'' criterion in 40 CFR 50.1(j), states must demonstrate that
reasonable controls were implemented to regulate or reduce emissions
regardless of whether the controls would have prevented
exceedances.\55\ Finally we note that the relevance of dust controls is
inherent in the District's own characterization of the ``event'' as the
combination of wind and dust entrainment from anthropogenic and
nonanthropogenic sources.\56\
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\53\ ``BACM is the maximum degree of emissions reduction of
PM10 and PM-10 precursors from a source * * * which is
determined on a case-by-case basis, taking into account energy,
environmental, and economic impacts and other costs, to be
achievable for such source through application of production
processes and available methods, systems, and techniques for control
of each such pollutant.'' General Preamble Addendum at 42010.
\54\ Merriam-Webster's Ninth New Collegiate Dictionary.
\55\ Similarly, EPA explained in the preamble to the EER that
analysis of exceptional events includes consideration of whether
anthropogenic activities have been controlled to the extent possible
through use of all reasonably available reasonable and appropriate
measures. 72 FR 13560, 13566, footnote 11.
\56\ E.g., September NED, p. 9.
---------------------------------------------------------------------------
As discussed in our 2009 EE decision, the State failed to
demonstrate that reasonable controls were implemented for anthropogenic
sources contributing to the exceedances, including recreational OHVs
and fallow agricultural fields.\57\ Nor does ARB or ICAPCD provide
convincing evidence in the NEDs or elsewhere to support the claim that
controls on these sources could not have either prevented the
exceedances or reduced emissions.
---------------------------------------------------------------------------
\57\ 2009 EE decision, section 4.2.
---------------------------------------------------------------------------
EE #2: ICAPCD (Attachment) further argues that the consequence of
EPA's action would be to require control measures beyond the area's
practical abilities--a result the EER is specifically designed to
avoid. ICAPCD claims that other specific provisions are in place to
prevent such difficulties, and ICAPCD quotes from EPA guidance: ``If
emissions from anthropogenic sources are reduced to the point that it
is no longer technologically or economically feasible to reduce those
emissions further, and the area still cannot attain the NAAQS, the EPA
may consider waiving the serious area attainment date and appropriate
serious area requirements.'' \58\
---------------------------------------------------------------------------
\58\ General Preamble Addendum at 42008.
---------------------------------------------------------------------------
Response: The provisions to which ICAPCD refers are contained in
CAA section 188(f) which authorizes EPA to waive subpart 4 requirements
applicable to serious PM10 nonattainment areas, including
BACM, where EPA determines that anthropogenic sources of
PM10 do not contribute significantly to the violation of the
standard in the area. Under section 188(f), EPA may
[[Page 39373]]
also waive a specific date for attainment of the PM10
standard if the Administrator determines that nonanthropogenic sources
contribute significantly to a violation of the standard.
In guidance, EPA has established the same test for determining what
constitutes a significant contribution for section 188(f) as is used
for determining the sources for which BACM must be implemented under
CAA section 189(b)(1)(B).\59\ The passage in the guidance, quoted in
isolation by ICAPCD, is preceded by a lengthy discussion regarding the
circumstances under which a serious area such as Imperial County could
qualify for section 188(f) waivers. That discussion makes clear that
before EPA will consider waiving a serious area attainment date and
requirements for a serious area that failed to attain the standard by
the serious area deadline, the State must demonstrate that BACMs for
significant anthropogenic sources have been implemented and that the
area cannot attain the NAAQS with the implementation of additional
control measures to achieve at least 5% annual emission reductions
pursuant to CAA section 189(d). As discussed above and in the
proposal,\60\ ICAPCD has not shown that BACM has been implemented as
required by CAA section 189(b)(1)(B) for all significant source
categories in Imperial County.\61\ Thus it would be difficult to show
that additional controls are ``beyond the area's practical abilities''
or ``no longer technologically or economically feasible'' without a
more thorough BACM analysis.
---------------------------------------------------------------------------
\59\ Id. at 42004.
\60\ 75 FR 8008, 8010-8012 and proposal TSD, pp. 7-11.
\61\ The 2009 PM10 SIP for Imperial County that is
intended to address the 5% requirement in CAA section 189(d) was
adopted by ICAPCD in August 2009 but has not been submitted to EPA
by ARB. The plan concludes that the area would have attained the
PM10 standard by the end of 2008 but for transported
emissions from Mexico and with the ``exclusion of PM10
measurements affected by high-wind exceptional events.'' As a result
of the claimed exceptional events, with which we did not concur in
our 2009 EE decision, the plan also concludes that ``[t]he 5% yearly
emission reductions requirement does not apply to future years.''
2009 PM10 SIP, section 5.3.
---------------------------------------------------------------------------
EE #3: ICAPCD (Attachment) believes, citing the preamble to the
EER, that the rule only requires reasonable controls for anthropogenic
sources within the State.
Response: While Imperial County air quality may be affected by
emission sources from areas outside California, such as Arizona and
Mexico, our 2009 EE decision relies on the lack of demonstrated
controls for anthropogenic sources within California.
EE #4: ICAPCD (Attachment) believes that EPA has not specified
criteria for defining de minimis anthropogenic sources in the EER
context, explained how the EER justifies such criteria, or described
feasible analyses to implement such criteria.
Response: As noted above, our 2009 EE decision stated that inherent
in the ``not reasonably controllable or preventable'' criterion of the
definition of ``exceptional event'' in 40 CFR 50.1(j) ``is a
requirement that the State demonstrate that anthropogenic sources
contributing to the exceedance caused by the event were reasonably
controlled.'' We also suggested that this requirement be limited to
``all non-de minimis anthropogenic sources.'' \62\ In this case,
however, rather than further interpreting the EER, we relied on
statements in the NEDs acknowledging anthropogenic contributions in
order to determine which anthropogenic sources were contributing to the
2006 and 2007 exceedances.\63\
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\62\ 2009 EE decision, section 4.2.
\63\ See id., section 4.2.1.
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EE #5: ICAPCD (Attachment) opposes the statement in EPA's 2009 EE
decision that ``because implementation of BACM is required in serious
PM10 areas such as Imperial County under section 189(b) of
the CAA, it is appropriate to consider that level of control in
evaluating whether reasonable controls are in place for purposes of the
Exceptional Events Rule.'' Specifically, ICAPCD argues that (1) such a
standard would create a new standard for exceptional event showings
that is inconsistent with the language and intent of the EER which
entails only ``reasonable'' and not ``best'' control of anthropogenic
sources; (2) the purpose of the EER is to protect states from
consequences of reclassification as a result of exceptional events; (3)
by definition, exceptional events fall outside the normal planning
process and their analysis should not depend on elements of the normal
planning process including designation status; and (4) the meaning of
``reasonable controls'' for the EER should not vary by an area's
nonattainment status and should not be as stringent as BACM.
Response: As stated in our 2009 EE decision and in the preamble to
the EER, EPA addresses the EER criteria, including that the event must
be ``not reasonably controllable or preventable,'' on a case-by-case
basis considering the weight of available evidence.\64\ Thus it is
appropriate to consider the totality of circumstances in Imperial
County in determining what constitutes ``reasonable'' controls. We note
again that the County has been designated nonattainment and classified
as moderate or serious since 1990. The area was reclassified to serious
in 2004.
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\64\ 2009 EE decision, pp. 4 and 7; 72 FR 13560, 13569.
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In evaluating rules as RACM or BACM, EPA has long considered it
appropriate to consider local conditions since what is technologically
and economically feasible in one area may not be in another.\65\
Moreover, EPA's 2009 EE decision did not define reasonable control as
BACM in all cases or suggest that the EER mandates such an outcome.
Rather, we stated that ``[b]ecause implementation of BACM is required
in serious PM10 nonattainment areas such as Imperial County
under CAA section 189(b), it is appropriate to consider that level of
control in evaluating whether reasonable controls are in place for
purposes of the Exceptional Events Rule.'' 66 67 While
ICAPCD states that this is inappropriate reliance on the normal
planning process, an area's nonattainment designation and
classification are inherently part of the local conditions that are
appropriately factored into what controls are reasonable for purposes
of the EER. We also noted that ARB had failed to demonstrate any
meaningful analysis of BACM or any other level of control for either
OHVs or fallow fields, despite apparent significant emissions and
available controls imposed elsewhere.\68\
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\65\ See 57 FR 13498, 13540-13541 (April 16, 1992) and the
General Preamble Addendum at 42010.
\66\ 2009 EE decision, section 4.2.2; 72 FR 70222.
\67\ We note that in EPA's Natural Events Policy which applied
prior to the EER, we stated that ``BACM must be implemented at
contributing anthropogenic sources of dust in order for PM-10 NAAQS
exceedances to be treated as due to uncontrollable natural events
under this policy.'' This requirement applied to moderate areas
which otherwise would not have been required to implement BACM at
all as well as to serious areas. Thus, while the EER does not
include such a mandate, it is entirely appropriate and consistent
with the Agenc