Approval and Promulgation of Implementation Plans; Montana; Libby 1997 Annual PM2.5, 74577-74588 [2022-26504]
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Federal Register / Vol. 87, No. 233 / Tuesday, December 6, 2022 / Proposed Rules
or in any other area where EPA or an
Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, this rule does not have
tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), because
redesignation is an action that affects
the status of a geographical area and
does not impose any new regulatory
requirements on tribes, impact any
existing sources of air pollution on
tribal lands, nor impair the maintenance
of ozone national ambient air quality
standards in tribal lands.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Oxides of nitrogen, Ozone, Volatile
organic compounds.
Dated: November 30, 2022.
Meghan A. McCollister,
Regional Administrator, Region 7.
74577
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart AA—Missouri
2. In § 52.1320, the table in paragraph
(e) is amended by adding the entry
‘‘(85)’’ to read as follows:
■
For the reasons stated in the
preamble, the EPA proposes to amend
40 CFR part 52 as set forth below:
§ 52.1320
*
Identification of plan.
*
*
(e) * * *
*
*
EPA-APPROVED MISSOURI NONREGULATORY SIP PROVISIONS
Applicable geographic or
nonattainment area
State
submittal
date
*
*
St. Louis Area: Missouri counties of
Jefferson, St. Charles, and St.
Louis along with the City of St.
Louis and Boles Township in
Franklin County.
*
9/8/2021, 4/
8/2022.
Name of nonregulatory
SIP provision
*
(85) Marginal Plan for
the St. Louis 2015 8Hour Ozone Nonattainment Area.
*
*
*
*
*
[FR Doc. 2022–26503 Filed 12–5–22; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 81
[EPA–R08–OAR–2021–0003; FRL–10454–
01–R8]
Approval and Promulgation of
Implementation Plans; Montana; Libby
1997 Annual PM2.5 Limited
Maintenance Plan and Redesignation
Request
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
The Environmental Protection
Agency (EPA or the Agency) is
proposing to take three separate but
related actions. First, EPA is proposing
to determine that the Libby fine
particulate matter (PM2.5) nonattainment
area (Libby Area) is attaining the 1997
annual PM2.5 national ambient air
quality standards (NAAQS or standard)
based on 2014–2021 data. The Agency
is also proposing to approve Montana’s
plan for maintaining the 1997 annual
PM2.5 NAAQS (limited maintenance
plan) and to redesignate the Libby Area
to attainment for the 1997 annual PM2.5
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SUMMARY:
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EPA approval date
Explanation
*
[Date of publication of
the final rule in the
Federal Register],
[Federal Register citation of the final rule].
*
*
This action approves the Marginal
nonattainment area plan for the
St. Louis Area for the 2015 8-hour
Ozone NAAQS
[EPA–R07–OAR–2022–0880; FRL–
10388–01–R7].
NAAQS, submitted by the State of
Montana on June 24, 2020.
DATES: Written comments must be
received on or before January 5, 2023.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R08–
OAR–2021–0003, to the Federal
Rulemaking Portal at https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Once submitted, comments cannot be
edited or removed from
www.regulations.gov. EPA may publish
any comment received to its public
docket. Do not submit electronically any
information you consider to be
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Multimedia
submissions (audio, video, etc.) must be
accompanied by a written comment.
The written comment is considered the
official comment and should include
discussion of all points you wish to
make. EPA will generally not consider
comments or comment contents located
outside of the primary submission (i.e.,
on the web, cloud, or other file sharing
system). For additional submission
methods, the full EPA public comment
policy, information about CBI or
multimedia submissions, and general
guidance on making effective
comments, please visit https://
www2.epa.gov/dockets/commentingepa-dockets.
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Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. Publicly
available docket materials are available
electronically in www.regulations.gov.
To reduce the risk of COVID–19
transmission, for this action we do not
plan to offer hard copy review of the
docket. Please email or call the person
listed in the FOR FURTHER INFORMATION
CONTACT section if you need to make
alternative arrangements for access to
the docket.
FOR FURTHER INFORMATION CONTACT:
Amrita Singh, Air and Radiation
Division, U.S. Environmental Protection
Agency (EPA), Region 8, Mail Code
ARD–QP, 1595 Wynkoop Street, Denver,
Colorado 80202–1129, telephone
number: (303) 312–6103, email address:
singh.amrita@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document wherever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
EPA.
Table of Contents
I. What are the actions EPA is proposing to
take?
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II. What is the background for EPA’s
proposed actions?
A. The PM2.5 NAAQS
B. Designation of PM2.5 NAAQS
Nonattainment Areas
C. PM2.5 NAAQS Nonattainment Area
Planning Requirements
D. Limited Maintenance Plans
III. Why is EPA proposing these actions?
IV. What is EPA’s analysis of the request?
A. Has the State met all applicable
requirements under section 110 and part
D of the Clean Air Act (CAA) and have
those requirements been fully approved?
(CAA sections 107(d)(3)(E)(ii) and (v))
B. Has the State demonstrated that air
quality improvement is due to
permanent and enforceable reductions?
C. Does the area have a fully approved
maintenance plan pursuant to section
175A of the CAA?
D. Transportation and General Conformity
V. What are the effects of EPA’s proposed
actions?
VI. Proposed Actions
VII. Statutory and Executive Order Reviews
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I. What are the actions EPA is
proposing to take?
EPA is proposing to take the following
separate but related actions: (1) to
determine that the Libby Area is
attaining the 1997 annual PM2.5 NAAQS
based on 2014–2021 data; (2) to approve
Montana’s plan for maintaining the
1997 annual PM2.5 NAAQS (limited
maintenance plan); and (3) to
redesignate the Libby Area to attainment
for the 1997 annual PM2.5 NAAQS.
Libby, Montana is a small rural
community located in Lincoln County
in the northwestern part of the State.
Libby sits in the narrow, triangular
Kootenai valley at an elevation of 2,100
feet. The Libby Area is dominated by
three major mountain ranges that limit
the air-shed: (1) the Rocky Mountain
and Flathead Ranges on the eastern
boundary; (2) the Purcell Range, which
roughly bisects the area from north to
south; and (3) the Selkirk and Cabinet
Ranges on the western boundary. Most
of the area surrounding Libby, Montana
is national forest land managed by the
U.S. Forest Service.
These proposed actions are
summarized and described in greater
detail throughout this proposed
rulemaking. EPA’s 1997 annual PM2.5
nonattainment designation for the Libby
Area triggered an obligation for Montana
to develop a nonattainment state
implementation plan (SIP) revision
addressing certain Clean Air Act (CAA)
requirements under title I, part D,
subpart 1 (hereinafter ‘‘Subpart 1’’) and
title I, part D, subpart 4 (hereinafter
‘‘Subpart 4’’). Subpart 1 contains the
general requirements for nonattainment
areas for criteria pollutants, including
requirements to develop a SIP that
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provides for the implementation of
reasonably available control measures
(RACM) under section 172(c)(1),
reasonable further progress (RFP),
includes base-year and attainment-year
emissions inventories, and for the
implementation of contingency
measures. As discussed in greater detail
later in this document, Subpart 4
contains specific planning and
scheduling requirements for coarse
particulate matter (PM10) nonattainment
areas, including requirements for new
source review (NSR), RACM (under
CAA section 189(a)(1)(C)), and RFP.
EPA’s longstanding general guidance
interpreting the 1990 CAA
Amendments, known as the General
Preamble, EPA discussed the
relationship of Subpart 1 and Subpart 4
SIP requirements and pointed out that
Subpart 1 requirements were to an
extent ‘‘subsumed by, or integrally
related to, the more specific PM–10
requirements.’’ See 57 FR 13538 (April
16, 1992). In addition, under the United
States Court of Appeals for the District
of Columbia Circuit’s (D.C. Circuit’s)
January 4, 2013, decision in Natural
Resources Defense Council (NRDC) v.
EPA, 706 F.3d 428 (D.C. Cir. 2013),
Subpart 4 requirements apply to PM2.5
nonattainment areas.1
On June 2, 2014 (79 FR 31566), EPA
published a rule entitled ‘‘Identification
of Nonattainment Classification and
Deadlines for Submission of State
Implementation Plan (SIP) Provisions
for the 1997 Fine Particle (PM2.5)
National Ambient Air Quality Standard
(NAAQS) and 2006 PM2.5 NAAQS’’
(‘‘Classification and Deadlines Rule’’).
In that rule, the Agency responded to
the D.C. Circuit’s January 2013 decision
by identifying all PM2.5 nonattainment
areas for the 1997 and 2006 PM2.5
NAAQS as ‘‘Moderate’’ nonattainment
areas under Subpart 4, and by
establishing a new SIP submission date
of December 31, 2014, for Moderate area
attainment plans and for any additional
attainment-related or nonattainment
new source review plans necessary for
areas to comply with the requirements
applicable under Subpart 4. Id. at
31567–70.
EPA is proposing to determine that
the Libby Area is attaining the 1997
1 In explaining its decision, the Court reasoned
that the plain meaning of the CAA requires
implementation of the 1997 PM2.5 NAAQS under
Subpart 4 because PM2.5 particles fall within the
statutory definition of PM10 and are thus subject to
the same statutory requirements. EPA finalized its
interpretation of Subpart 4 requirements as applied
to the PM2.5 NAAQS in its final rule entitled ‘‘Fine
Particulate Matter National Ambient Air Quality
Standards: State Implementation Plan
Requirements; Final Rule’’ (81 FR 58010, August
24, 2016).
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annual PM2.5 NAAQS based on recent
air quality data. EPA is also proposing
to approve Montana’s limited
maintenance plan (LMP) for the Libby
Area as meeting the requirements of
section 175A of the CAA.
EPA also proposes to determine that
the Libby Area has met the requirements
for redesignation under section
107(d)(3)(E) of the CAA. This proposed
rulemaking is in response to Montana’s
June 24, 2020 redesignation request and
associated SIP submission that address
the requirements described in section
107(d)(3)(E) of the CAA for the
redesignation of the Libby Area from
nonattainment to attainment for the
1997 annual PM2.5 NAAQS.2
II. What is the background for EPA’s
proposed actions?
A. The PM2.5 NAAQS
Particulate matter includes particles
with diameters that are generally 2.5
microns or smaller (PM2.5) and particles
with diameters that are generally 10
microns or smaller (PM10). PM2.5
contributes to effects that are harmful to
human health and the environment,
including premature mortality,
aggravation of respiratory and
cardiovascular disease, decreased lung
function, visibility impairment, and
damage to vegetation and ecosystems.
Individuals particularly sensitive to
PM2.5 exposure include older adults,
people with heart and lung disease, and
children. See 78 FR 3086 at 3088
(January 15, 2013). PM2.5 can be emitted
directly into the atmosphere as a solid
or liquid particle (‘‘primary PM2.5’’ or
‘‘direct PM2.5’’) or can be formed in the
atmosphere (‘‘secondary PM2.5’’) as a
result of various chemical reactions
among precursor pollutants such as
nitrogen oxides (NOX), sulfur oxides
(SOX), volatile organic compounds
(VOCs), and ammonia (NH3).3
Under section 109 of the CAA, EPA
has established national ambient air
quality standards for certain pervasive
air pollutants (referred to as ‘‘criteria
pollutants’’) and conducts periodic
reviews of the NAAQS to determine
whether they should be revised or
whether new NAAQS should be
established. EPA sets the NAAQS for
criteria pollutants at levels required to
protect public health and welfare.4
2 See Libby Area SIP submission, available in the
docket for this proposed rulemaking.
3 EPA, Air Quality Criteria for Particulate Matter,
No. EPA/600/P–99/002aF and EPA/600/P–99/
002bF, October 2004.
4 For a given air pollutant, ‘‘primary’’ national
ambient air quality standards are those determined
by EPA as requisite to protect the public health.
‘‘Secondary’’ standards are those determined by
EPA as requisite to protect the public welfare from
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PM2.5 is one of the ambient pollutants
for which EPA has established healthbased standards.
On July 18, 1997 (62 FR 38652), EPA
revised the NAAQS for particulate
matter to add new standards for PM2.5.
The Agency established primary and
secondary annual and 24-hour
standards for PM2.5. The annual
standard was set at 15.0 micrograms per
meter cubed (mg/m3) based on a 3-year
average of annual mean PM2.5
concentrations, and the 24-hour (daily)
standard was set at 65 mg/m3 based on
the 3-year average of the annual 98th
percentile values of 24-hour PM2.5
concentrations at each populationoriented monitor within an area.5
On October 17, 2006 (71 FR 61144),
EPA retained the annual average
NAAQS at 15.0 mg/m3 but revised the
level of the 24-hour PM2.5 NAAQS to 35
mg/m3 based on a 3-year average of the
annual 98th percentile values of 24-hour
concentrations.6
On December 14, 2012, EPA
promulgated the 2012 PM2.5 NAAQS,
including a revision of the annual
standard to 12.0 mg/m3 based on a 3-year
average of annual mean PM2.5
concentrations. The Agency maintained
the 24-hour standard of 35 mg/m3 based
on a 3-year average of the 98th
percentile of 24-hour concentrations.
See 78 FR 3086 (January 15, 2013).
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B. Designation of PM2.5 NAAQS
Nonattainment Areas
Following promulgation of a new or
revised NAAQS, EPA is required by
CAA section 107(d) to designate areas
throughout the nation as attaining or not
attaining the NAAQS. On January 5,
2005 (70 FR 944), EPA published area
designations for the 1997 PM2.5 NAAQS
based on air quality data for the
calendar years 2001–2003. In that
rulemaking, EPA designated Libby,
Montana as nonattainment for the 1997
annual PM2.5 NAAQS. These
designations became effective on April
5, 2005.
On March 17, 2011 (76 FR 14584),
EPA approved Montana’s attainment
plan which included an attainment
demonstration, an analysis of reasonable
available control technology/reasonable
any known or anticipated adverse effects associated
with the presence of such air pollutant in the
ambient air. CAA section 109(b).
5 The primary and secondary standards were set
at the same level for both the 24-hour and the
annual PM2.5 standards.
6 Under EPA regulations at 40 CFR part 50, the
primary and secondary 2006 24-hour PM2.5 NAAQS
are attained when the annual arithmetic mean
concentration, as determined in accordance with 40
CFR part 50, appendix N, is less than or equal to
35 mg/m3 at all relevant monitoring sites in the
subject area, averaged over a 3-year period.
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available control measure (RACT/
RACM), base-year and projection year
inventories, and contingency measures
for the 1997 PM2.5 NAAQS for the Libby
Area. On July 14, 2015 (80 FR 40911),
EPA finalized its determination that the
Libby Area attained the 1997 annual
PM2.5 NAAQS by the Area’s statutory
attainment date of December 31, 2011.
This determination was based upon
quality-assured and certified ambient air
monitoring data for the 2007–2009
monitoring period that demonstrated
that the Libby Area attained the 1997
annual PM2.5 NAAQS by the attainment
date. In the same rulemaking, EPA also
issued a clean data determination under
the Agency’s Clean Data Policy 7 based
upon quality-assured and certified
ambient air monitoring data that
demonstrated the Libby Area continued
to attain the 1997 annual PM2.5 NAAQS
based on 2012–2014 monitoring data.8
On July 29, 2016, EPA issued a rule
entitled ‘‘Fine Particulate Matter
National Ambient Air Quality
Standards: State Implementation Plan
Requirements’’ (‘‘PM2.5 SIP
Requirements Rule’’). See 81 FR 58010
(August 24, 2016). This rule clarifies
how states should meet the statutory SIP
requirements that apply to areas
designated nonattainment for any PM2.5
NAAQS under Subparts 1 and 4. It does
so by establishing regulatory
requirements and by providing guidance
that is applicable to areas that are
currently designated nonattainment for
existing PM2.5 NAAQS and areas that
are designated nonattainment for any
PM2.5 NAAQS in the future. In addition,
the rule responds to the D.C. Circuit’s
remand of the 1997 PM2.5
Implementation Rules. As a result, the
requirements of the rule also govern
future actions associated with states’
ongoing implementation efforts for the
1997 and 2006 PM2.5 NAAQS. In the
PM2.5 SIP Requirements Rule, EPA
revoked the 1997 primary annual PM2.5
NAAQS in areas that had always been
attainment for that NAAQS, and in areas
that had been designated as
nonattainment but that were
redesignated to attainment before
October 24, 2016, the PM2.5 SIP
Requirements Rule effective date. See 81
FR 58010 (August 24, 2016).
7 See e.g., 70 FR 71612 (November 29, 2005) and
72 FR 20586 (April 25, 2007).
8 See 71 FR 19935 (April 14, 2015) that addresses
the final clean data determination and a final
determination of attainment by the attainment date
for the Libby nonattainment area. As part of its
clean data determination submission to EPA,
Montana submitted the clean data determination to
address the national ambient air requirements
under Subpart 4.
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74579
In the August 24, 2016 final rule, EPA
also finalized a provision to revoke the
1997 primary annual PM2.5 NAAQS in
areas redesignated to attainment after
October 24, 2016, on the effective date
of an area’s redesignation. See 40 CFR
50.13(d). If this proposal is finalized, the
1997 primary annual PM2.5 NAAQS will
be revoked for the Libby Area on the
effective date of the redesignation.
Beginning on that date, the Area will no
longer be subject to transportation or
general conformity requirements for the
1997 annual PM2.5 NAAQS due to
revocation of the primary NAAQS. See
81 FR 58125–6. If redesignated, the
Libby Area will be required to
implement the maintenance plan
requirements under section 175A for the
1997 annual PM2.5 NAAQS, and the
prevention of significant deterioration
(PSD) program for the 1997 annual
PM2.5 NAAQS. Once approved, the
maintenance plan can only be revised if
the revision meets the requirements of
CAA section 110(l) and, if applicable,
CAA section 193. As described in the
PM2.5 SIP Requirements Rule, those
1997 annual PM2.5 maintenance areas
with a revoked NAAQS are no longer
required to submit a second 10-year
maintenance plan for the 1997 annual
PM2.5 NAAQS. See 81 FR 58144.
C. PM2.5 NAAQS Nonattainment Area
Planning Requirements
The CAA establishes the requirements
for redesignation of an area from
nonattainment to attainment.
Specifically, section 107(d)(3)(E) allows
for redesignation of areas from
nonattainment to attainment provided
that the following criteria are met:
(1) The Administrator has determined
that the area has attained the applicable
NAAQS;
(2) The Administrator has fully
approved the applicable SIP for the area
under section 110(k) of the CAA;
(3) The Administrator has determined
that the improvement in air quality is
due to permanent and enforceable
reductions in emissions;
(4) The Administrator has fully
approved a maintenance plan for the
area as meeting the requirements of
section 175A of the CAA; and
(5) The state containing the area has
met all requirements applicable to the
area under section 110 and part D of the
CAA.
Section 110 of the CAA identifies a
comprehensive list of elements that SIPs
must include, and part D establishes the
SIP requirements for nonattainment
areas. The generally applicable
nonattainment SIP requirements are
found in part D, subpart 1, and the
particulate matter-specific SIP
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requirements are found in part D,
subpart 4.
On April 16, 1992 (57 FR 13498), EPA
provided guidance on redesignation in
the General Preamble for the
Implementation of Title I of the CAA
Amendments of 1990, and the Agency
supplemented this guidance on April
28, 1992 (57 FR 18070). EPA has
provided further guidance on processing
redesignation requests in the following
documents:
1. ‘‘Procedures for Processing Requests to
Redesignate Areas to Attainment,’’
Memorandum from John Calcagni, Director,
Air Quality Management Division, September
4, 1992 (hereinafter referred to as the
‘‘Calcagni Memorandum’’);
2. ‘‘State Implementation Plan (SIP)
Actions Submitted in Response to Clean Air
Act (CAA) Deadlines,’’ Memorandum from
John Calcagni, Director, Air Quality
Management Division, October 28, 1992; and
3. ‘‘Part D New Source Review (Part D
NSR) Requirements for Areas Requesting
Redesignation to Attainment,’’ Memorandum
from Mary D. Nichols, Assistant
Administrator for Air and Radiation, October
14, 1994 (hereinafter referred to as the
‘‘Nichols Memorandum’’).
D. Limited Maintenance Plans
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CAA section 175A(a) requires that
nonattainment areas seeking
redesignation to attainment submit ‘‘a
revision of the applicable state
implementation plan to provide for the
maintenance of the [NAAQS] for such
air pollutant in the area concerned for
at least 10 years after the redesignation.’’
EPA explained in the Calcagni
Memorandum that states may meet this
requirement to ‘‘provide for the
maintenance of the NAAQS’’ by using
projected emissions inventories or air
quality modeling showing continued
maintenance until the end of the
relevant maintenance period. See
Calcagni Memorandum at 9–11. EPA
clarified in three subsequent guidance
memos that certain areas could meet the
CAA section 175A requirement to
provide for maintenance by
demonstrating that the area’s design
value was well below the NAAQS and
that the historical stability of the area’s
air quality levels showed that the area
was unlikely to violate the NAAQS in
the future.9 The Agency refers to this
streamlined demonstration of
9 See ‘‘Limited Maintenance Plan Option for
Nonclassifiable Ozone Nonattainment Areas’’ from
Sally L. Shaver, Office of Air Quality Planning and
Standards (OAQPS), dated November 16, 1994;
‘‘Limited Maintenance Plan Option for
Nonclassifiable CO Nonattainment Areas’’ from
Joseph Paisie, OAQPS, dated October 6, 1995;
Copies of these guidance memoranda can be found
in the docket for this proposed rulemaking.
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maintenance as a limited maintenance
plan.
EPA has interpreted CAA section
175A as permitting this option because
section 175A does not define how areas
may demonstrate maintenance, and in
EPA’s experience with implementing
the various NAAQS, areas that qualify
for an LMP and have approved LMPs,
have rarely, if ever, experienced
subsequent violations of the NAAQS. As
noted in the LMP guidance memoranda,
states seeking an LMP must still submit
the other maintenance plan elements
outlined in the Calcagni Memorandum,
including an attainment emissions
inventory, provisions for the continued
operation of the ambient air quality
monitoring network, verification of
continued attainment, and a
contingency plan in the event of a future
violation of the NAAQS. Moreover,
states seeking to do an LMP must still
submit a CAA section 175A
maintenance plan as a revision to the
SIP, with all attendant notice and
comment procedures. While the LMP
guidance memoranda were originally
written with respect to certain
NAAQS,10 EPA has extended the LMP
interpretation of section 175A to other
NAAQS and pollutants not specifically
covered by the previous guidance
memos.11
To determine the LMP eligibility
criteria for the Libby Area, EPA is
interpreting the requirements as
described in the 2001 memorandum
from Lydia Wegman 12 regarding LMPs
for PM10 areas as applying to PM2.5. This
memorandum states that one way for a
PM10 area to qualify for an LMP is to
show that the area’s average design
value (ADV) (based upon the most
recent 5 years of monitoring data) is at
or below the critical design value (CDV).
The memorandum defines the CDV as
an indicator of the likelihood of future
violations of the NAAQS in an area
given the area’s current ADV and its
historical variability and provides a
means for calculating the CDV for an
area (or monitoring site) (Attachment A
of the 2001 Wegman Memorandum).
The CDV is the highest average design
value an area could have before it may
10 The prior memos addressed unclassifiable
areas under the 1-hour ozone NAAQS,
nonattainment areas for the PM10 NAAQS, and
nonattainment areas for the carbon monoxide
NAAQS.
11 See, e.g., 79 FR 41900 (July 18, 2014) (approval
of second ten-year LMP for Grant County 1971
sulfur dioxide maintenance area).
12 ‘‘Limited Maintenance Plan Option for
Moderate PM10 Nonattainment Areas’’ from Lydia
Wegman, OAQPS, dated August 9, 2001 (hereinafter
referred to as the ‘‘Wegman Memorandum’’). A
copy of this guidance memorandum can be found
in the docket for this proposed rulemaking.
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experience a future violation of the
NAAQS with a certain probability—in
the case of the Wegman Memorandum,
a probability of 1 in 10. Therefore, if an
area’s current ADV is less than the
area’s CDV, that area has a less than 1
in 10 chances of violating the NAAQS
in the future. As noted in Attachment A
of the Wegman Memorandum, the CDV
calculation was designed to apply for
any NAAQS pollutant and is not
specific to PM10. Montana employed
this methodology to demonstrate that
the Libby Area is eligible for an LMP
and that the plan therefore provides for
maintenance of the NAAQS for 10 years
following redesignation. We agree that
the State’s demonstration meets the
requirements of CAA section 175A and
shows that the Area will continue to
maintain the annual PM2.5 NAAQS
following redesignation through 2031.
In its SIP submission, Montana used a
site-specific CDV calculated with PM2.5
data from the one ambient design value
monitor in the Libby Area.
The 2001 Wegman Memorandum also
provided that an LMP was appropriate
only for those PM10 areas that were
expecting limited growth of on-road
motor vehicle emissions (including
fugitive dust), and therefore included a
motor vehicle regional emissions
analysis demonstration that states
seeking a PM10 LMP should perform
(Attachment B to the Wegman
Memorandum). According to the
Wegman Memorandum, the
demonstration should show that the
ADV remains below the margin of safety
provided for in the memorandum, even
after the growth of on-road motor
vehicle emissions is considered. This
proposed rulemaking uses the sitespecific CDV instead of the margin of
safety described in the Wegman
Memorandum for this analysis as EPA
has not recommended a margin of safety
for the 1997 annual PM2.5 NAAQS.
III. Why is EPA proposing these
actions?
On June 24, 2020, the State of
Montana requested that EPA redesignate
the Libby Area to attainment for the
1997 annual PM2.5 NAAQS and
submitted an associated SIP revision
containing an LMP. EPA’s evaluation of
the plan and air quality data indicates
that the Libby Area meets the
requirements for redesignation set forth
in section 107(d)(3)(E) of the CAA,
including that the LMP fulfills the
maintenance plan requirements under
section 175A of the CAA. As a result of
these findings, EPA is proposing to take
the separate but related actions to
approve the LMP and redesignate the
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Libby Area from nonattainment to
attainment.
IV. What is EPA’s analysis of the
request?
To redesignate an area from
nonattainment to attainment, the CAA
requires EPA to determine that the area
has attained the applicable NAAQS
(CAA section 107(d)(3)(E)(i)). The
criteria for determining if an area is
attaining the 1997 annual PM2.5 NAAQS
is set out in 40 CFR 50.13 and 40 CFR
part 50, appendix N. The 1997 annual
PM2.5 primary and secondary standards
are met when the annual design value 13
at each eligible monitoring site within
the area is less than or equal to 15.0 mg/
m3.
Based on data from 2007–2009, EPA
determined that the Libby Area attained
the 1997 annual PM2.5 standard by
December 31, 2011, well before its
attainment date of July 14, 2015.14 In
addition, EPA issued a final clean data
determination under the Clean Data
Policy that the Libby Area was attaining
the 1997 annual PM2.5 NAAQS, based
on quality-assured and certified ambient
air quality data for the 2012–2014
monitoring period. The Libby Area has
continued to attain the 1997 annual
PM2.5 NAAQS since EPA’s earlier
determinations that the Area attained
the NAAQS.
The Libby Area has one State and
Local Air Monitoring Station (SLAMS)
monitor operated by the Montana
Department of Environmental Quality
(MDEQ). This monitor (Air Quality
System (AQS) Site ID 30–53–0018) has
complete data for 2014–2021, which is
the period of data utilized for this
proposed redesignation.15
Table 1 summarizes the annual mean
PM2.5 data collected from 2014–2021 for
the Libby Area.16 Table 2 shows the
annual design values for 2016–2021.
The data presented in the tables were
calculated from all data available in
AQS, including those data flagged by
the State of Montana as potentially
influenced by exceptional events. EPA
deems these data valid as they are
complete and have been certified by
MDEQ.
None of the annual design values
from 2016–2021 from the Libby Area
monitoring site exceed the 1997 annual
PM2.5 NAAQS of 15.0 mg/m3, and as
such, EPA proposes to determine that
the Libby Area has attained the 1997
annual PM2.5 NAAQS, and therefore
meets the requirement of CAA section
107(d)(3)(E)(i).
TABLE 1—PM2.5 ONE-YEAR ANNUAL MEAN CONCENTRATIONS 17
Year:
2014
2015
2016
2017
2018
2019
2020
2021
Concentration (μg/m3) ......................................................................
9.3
14.9
9.8
14.3
14.6
11.4
13.8
14.6
TABLE 2—PM2.5 ANNUAL DESIGN VALUE 18
3-Year Period:
2014–2016
2015–2017
2016–2018
2017–2019
2018–2020
2019–2021
Design Value (μg/m3) ......................................................
11.4
13.0
12.9
13.4
13.3
13.3
A. Has the State met all applicable
requirements under section 110 and
part D of the Clean Air Act (CAA) and
have those requirements been fully
approved? (CAA sections 107(d)(3)(E)(ii)
and (v))
Sections 107 (d)(3)(E)(ii) and (v)
require EPA to determine that the area
has a fully approved applicable SIP
under section 110(k) that meets all the
basic applicable requirements under
section 110 and part D for purposes for
redesignation. The following is a
summary of how Montana meets these
requirements.
1. CAA Section 110 Requirements
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Section 110(a)(2) of title I of the CAA
delineates the general requirements for
a SIP, which include enforceable
emissions limitations and other control
measures, means or techniques,
provisions for the establishment and
13 The Annual PM
2.5 NAAQS design value is the
3-year average of PM2.5 annual mean mass
concentrations. These annual means are calculated
as the weighted arithmetic mean of the four quarters
of valid data at the site and the annual means are
only considered valid when they meet data
completeness requirements detailed in 40 CFR
50.13. Once three valid annual means are available,
they can be averaged together to determine the
annual design value for that site.
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operation of appropriate devices
necessary to collect data on ambient air
quality, and programs to enforce
limitations. The general SIP elements
and requirements set forth in CAA
section 110(a)(2) include, but are not
limited to the following:
• Submittal of a SIP that has been
adopted by the state after reasonable
public notice and hearing;
• Provisions for establishment and
operation of appropriate procedures
needed to monitor ambient air quality;
• Implementation of a source permit
program;
• Provisions for the implementation
of part C requirements (PSD);
• Provisions for the implementation
of part D requirements for NSR permit
programs;
• Provisions for air pollution
modeling; and
14 See
80 FR 40911.
criteria for determining if an area is
attaining the 1997 Annual PM2.5 NAAQS are set out
in the 40 CFR 50.13 and 40 CFR part 50, appendix
N. Three years of valid annual means are required
to produce a valid annual standard design value. A
year meets data completeness requirements when at
least 75 percent of the scheduled sampling days for
each quarter have valid data.
15 The
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• Provisions for public and local air
agency participation in planning and
emission control rule development.
CAA section 110(a)(2)(D) requires that
SIPs contain certain measures to prevent
sources in a state from significantly
contributing to air quality problems in
another state; the portion of a state’s SIP
that include these measures is known as
an interstate transport SIP. However,
these CAA section 110(a)(2)(D)
requirements apply to a state and are
not linked with a particular
nonattainment area’s designation and
classification in that state. The interstate
transport SIP submittal requirements,
where applicable, continue to apply to
a state regardless of the designation of
any one area in the state. Thus, EPA has
determined that these requirements are
not applicable requirements for
purposes of redesignation. Instead, EPA
has determined that the requirements
16 The annual averages in Table 1 are calculated
by averaging the four quarters of data.
17 Annual mean concentration is the averaging of
four complete quarters of data for each year. See 40
CFR part 50, appendix N.
18 The Annual PM
2.5 NAAQS design value is the
3-year average of PM2.5 annual mean mass
concentrations. See 40 CFR 50.13.
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linked with a particular nonattainment
area’s designation and classifications are
the relevant measures, i.e., the
requirements that must be met, for EPA
to redesignate an area.
In addition, EPA has determined that
the other CAA section 110(a)(2)
elements not connected with
nonattainment plan submissions and
not linked with an area’s attainment
status are not applicable requirements
for purposes of redesignation because
the area will still be subject to these
requirements after it is redesignated.
EPA concludes that the CAA section
110(a)(2) and part D requirements,
which are linked with a particular area’s
designation and classification, are the
relevant measures to evaluate in
reviewing a redesignation request, and
that section 110(a)(2) elements not
linked to the area’s nonattainment status
are not applicable for purposes of
redesignation. EPA has applied this
interpretation consistently in many
redesignations.19
EPA’s review of the Montana SIP
shows that the State has satisfied the
general SIP requirements under section
110(a)(2) of the CAA, to the extent they
are applicable for the purposes of
redesignation. Moreover, EPA has
previously approved provisions of
Montana’s SIP as demonstrating
compliance with the CAA section
110(a)(2) requirements for the 1997
annual PM2.5 NAAQS. See 78 FR 45864
(July 30, 2013). Therefore, EPA proposes
to determine that MDEQ has met all
general SIP requirements for the Libby
Area that are applicable for purposes of
redesignation under section 110 of the
CAA.
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2. Part D Requirements
Subparts 1 and 4 of part D, title 1 of
the CAA contain air quality planning
requirements for PM2.5 nonattainment
areas. Subpart 1 contains general
requirements for all nonattainment areas
of any pollutant, including PM2.5,
governed by a NAAQS. Subpart 1
requirements include, among other
things, provisions for RACM, RFP,
19 See, e.g., 81 FR 4420 (July 17, 2006) (final
redesignation for the Sullivan County, Tennessee
area); 79 FR 43655 (July 28, 2014) (final
redesignation for Bellefontaine, Ohio lead
nonattainment area); 61 FR 53174–53176 (October
10, 1996) and 62 FR 24826 (May 7 1997) (proposed
and final redesignation of Reading, Pennsylvania
ozone nonattainment area); 61 FR 20458 (May 7
1996) (final redesignation for Cleveland-AkronLorain, Ohio ozone nonattainment area); 60 FR
62748 (December 7, 1995) (final redesignation of
Tampa, Florida ozone nonattainment area); See also
65 FR 37879, 37890, (June 19, 2000) (discussing this
issue in final redesignation of Cincinnati, Ohio 1hour ozone nonattainment area); and 66 FR 50399
(October 19, 2001) (final redesignation of Pittsburg,
Pennsylvania 1-hour ozone nonattainment area).
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emissions inventories, contingency
measures, transportation conformity and
general conformity. Subpart 4 contains
specific planning and scheduling
requirements for PM2.5 nonattainment
areas. Sections 189(a), (c), (e)
requirements apply specifically to
Moderate PM2.5 nonattainment areas
and include an approved permit
program for construction of new and
modified major stationary sources,
provisions for RACM, an attainment
demonstration, quantitative milestones
demonstrating RFP toward attainment
by the applicable attainment date, and
provisions to ensure that the control
requirements applicable to major
stationary sources of PM2.5 precursors,
except where the Administrator has
determined that such sources do not
contribute significantly to PM2.5 levels
that exceed the NAAQS in the area.
We address the applicability of these
requirements to this action in the
following sections.
3. Subpart 1, Section 172 Requirements
Section 172(c) contains general
requirements for nonattainment area
plan provisions. A thorough discussion
of these requirements may be found in
the General Preamble. See 57 FR 13538
(April 16, 1992). EPA’s longstanding
interpretation is that certain planning
requirements designed to get a
nonattainment area to attainment of the
NAAQS are not ‘‘applicable’’ for
purposes of CAA section 107(d)(3)(E)(ii)
and (v) and therefore need not be
approved into the SIP before EPA can
redesignate the area. In the General
Preamble, EPA set forth its
interpretation of applicable
requirements for purposes of evaluating
redesignation requests when an area is
attaining the standard. See 57 FR 13564.
EPA noted that requirements for RFP
and other measures designed to provide
for an area’s attainment do not apply in
evaluating redesignation because those
nonattainment planning requirements
‘‘have no meaning’’ for an area that is
attaining the standard. Id. This
interpretation is also set forth in the
Calcagni Memorandum.
EPA’s understanding of CAA section
172 also forms its basis on its Clean Data
Policy. Under the Clean Data Policy,
EPA promulgates a determination of
attainment, published in the Federal
Register, which is subject to notice-andcomment rulemaking, and this
determination formally suspends a
state’s obligation to submit most of the
attainment planning requirements that
would otherwise apply, including an
attainment demonstration and planning
SIPs to provide for RFP, RACM, and
contingency measures under CAA
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Sfmt 4702
section 179(c)(9). The Clean Data Policy
has been codified in regulations
regarding the implementation of the
ozone and PM2.5 NAAQS. See e.g., 70
FR 71612 (November 29, 2005) and 72
FR 20586 (April 25, 2007).
Because the Libby Area is attaining
the 1997 annual PM2.5 NAAQS, the
attainment planning obligations in CAA
section 172, including the requirement
to submit an attainment demonstration
and RACM (172(c)(1)), RFP (172(c)(2)),
and contingency measures (172(c)(9))
are not considered ‘‘applicable’’
requirements for redesignation purposes
under CAA section 107(d)(3)(E)(ii) and
(v). In any case, Montana submitted
these elements as part of the Moderate
SIP requirements on March 26, 2008,
and EPA approved them on March 17,
2011.20
Section 172(c)(3) of the CAA requires
a comprehensive, accurate, current
inventory of actual emissions from all
sources of relevant pollutant(s) in
nonattainment areas. EPA’s March 17,
2011 approval of Montana’s March 26,
2008 SIP submission included a 2005
base-year emissions inventory for the
Libby Area. Montana also included an
emissions inventory for calendar year
2014 with the June 24, 2020 SIP
submittal of the LMP for the Libby Area.
The 2001 Wegman Memorandum states
that an attainment inventory should
represent emissions during the same 5year period associated with the air
quality data used to determine that the
area meets the requirements of the LMP
option. In addition, EPA reviewed an
updated 2017 emissions inventory 21 in
its analysis for the Libby PM2.5 LMP.
Section 172(c)(4) requires the
identification and quantification of
allowable emissions for major new and
modified stationary sources in an area,
and section 172(c)(5) and 189(a)(1)(A)
requires source permits for the
construction and operation of new and
modified major stationary sources
anywhere in the nonattainment area.
EPA approved the current Montana NSR
program for PM2.5 on July 18, 1995. See
60 FR 36715. Having a fully approved
nonattainment NSR program is not an
applicable requirement for this action;
nonetheless we have approved the
State’s program.22
Section 172(c)(7) requires the SIP
meet the applicable provisions of CAA
20 See
76 FR 14584.
in the docket for this proposed
rulemaking.
22 A detailed rationale for this view is described
in the memorandum from Mary Nichols, Assistant
Administrative for Air and Radiation, dated October
14, 1994, entitled, ‘‘Part D New Source Review
Requirements for Areas Requesting Redesignation
to Attainment.’’
21 Available
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applicable attainment date (section
189(c)); and (5) precursor control
(section 189(e)).
With respect to the specific
attainment planning requirements under
4. Subpart 1, Section 176 Conformity
Subpart 4,25 EPA applies the same
Requirements
interpretation that it applies to
Section 176(c) of the CAA requires
attainment planning requirements under
states to establish the criteria and
Subpart 1 or any other pollutant-specific
procedures to ensure that federally
subparts. That is, under its longsupported or funded projects conform to standing interpretation of the CAA,
the air quality planning goals in the
where an area is already attaining the
applicable SIP. The requirement to
standard, EPA does not consider those
determine conformity applies to
attainment planning requirements to be
transportation plans, programs and
applicable for purposes of evaluating a
projects that are developed, funded, or
request for redesignation, that is, CAA
approved under title 23 of the United
section 107(d)(3)(E)(ii) or (v), because
States Code (U.S.C.) and the Federal
requirements that are designed to help
Transit Act (transportation conformity)
an area achieve attainment no longer
as well as to other federally supported
have meaning where an area is already
or funded projects (general conformity). meeting the standard. EPA is therefore
State transportation conformity SIP
proposing to determine that the specific
revisions must be consistent with
attainment planning requirements under
federal conformity regulations relating
Subpart 4 are not applicable for
to consultation, enforcement, and
evaluating Montana’s redesignation
enforceability that EPA promulgated
request.
pursuant to its authority under the CAA.
CAA section 189(e) provides that
Although EPA interprets the
control requirements for major
23
conformity SIP requirements as not
stationary sources of direct PM10
applying for purposes of evaluating the
(including PM2.5) shall also apply to
redesignation request under section
particulate matter precursors from those
107(d)(3) 24 we note that Montana has an sources, except where EPA determines
approved conformity SIP. See 66 FR
that major stationary sources of such
48561 (September 21, 2001).
precursors do not contribute
significantly to PM10 levels that exceed
5. Subpart 4 Requirements
the standard in the area. The CAA does
As discussed in Section I of this
not explicitly address whether it would
document, in NRDC v. EPA, the D.C.
be appropriate to include a potential
Circuit held that EPA should have
exemption from precursor controls for
implemented the 1997 PM2.5 annual
all source categories under certain
NAAQS pursuant to the particulate
circumstances. In implementing Subpart
matter-specific provisions of Subpart 4.
4 with regard to controlling PM10, EPA
On remand, EPA identified all areas
permitted
states to determine that a
designated nonattainment for either the
precursor was ‘‘insignificant’’ where the
1997 or the 2006 PM2.5 NAAQS,
state could show in its attainment plan
including the Libby Area, as Moderate
nonattainment for purposes of Subpart 4 that it would expeditiously attain
without adoption of emission reduction
in the Classifications and Deadlines
Rule. Moderate nonattainment areas are measures aimed at that precursor. This
approach was upheld in the Association
subject to the requirements of CAA
of Irritated Residents v. EPA, 423 F.3d
sections 189(a), (c), and (e), including:
989 (9th Cir. 2005) and extended to
(1) an approved permit program for
construction of new and modified major PM2.5 implementation in the PM2.5 SIP
stationary sources (section 189(a)(1)(A)); Requirements Rule. A state may develop
its attainment plan and adopt RACM
(2) an attainment demonstration,
that target only those precursors that are
(section 189(a)(1)(B)); (3) provisions for
necessary to control for purposes of
RACM (section 189(a)(1)(C)); (4)
timely attainment. See 81 FR 58010 at
quantitative milestones demonstrating
58020 (August 24, 2016).
RFP toward attainment by the
For the Libby Area, a precursor
exemption
analysis under section 189(e)
23 CAA section 176(c)(4)(E) requires states to
and EPA’s implementing regulations is
submit revisions to their SIPs to reflect certain
not an applicable requirement that
federal criteria and procedures for determining
transportation conformity.
needs to be fully approved in the
24 EPA believes that this interpretation is
context of a redesignation under CAA
reasonable because state conformity rules are still
section 107(d)(3)(E)(ii) since the Area is
required after redesignation and federal conformity
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section 110(a)(2). EPA believes
Montana’s June 24, 2020 SIP submission
pertaining to the Libby Area meets the
requirements of section 110(a)(2).
rules apply where states rules have not been
approved. See Wall v. EPA, 265 F.3d 426 (6th Cir.,
2001) (upholding this interpretation); 60 FR 62748
(December 7, 1995).
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25 These planning requirements include the
attainment demonstration, qualitative milestone
requirements, and RACM analysis.
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74583
already in attainment which
demonstrates that precursors
contribution is insignificant. Therefore,
measures aimed at the precursors are
not needed.
As discussed previously in this
document, for areas that are attaining
the standard, EPA does not interpret
attainment planning requirements of
Subparts 1 and 4 to be applicable
requirements for purposes of
redesignating an area to attainment. On
July 14, 2015, EPA approved that the
Libby Area had attained the 1997
annual PM2.5 NAAQS by the Area’s
statutory attainment date. The Libby
Area has expeditiously attained the
1997 annual PM2.5 NAAQS, and
therefore, no additional controls of any
pollutant, including any PM2.5
precursor, are necessary to bring it into
attainment. In section V of this
document, we find that the Libby Area
continues to attain the NAAQS. EPA has
determined that the Libby Area has
attained the standard due to permanent
and enforceable emissions reductions.
Further, as set forth in section IV.C of
this document, we believe that the
Libby PM2.5 LMP demonstrates
continued maintenance of the 1997
annual PM2.5 NAAQS standard through
2031 which also demonstrates that the
PM2.5 precursors are insignificant.
Taken together, these factors support
our conclusion that PM2.5 precursors are
adequately controllable.
B. Has the state demonstrated that air
quality improvement is due to
permanent and enforceable reductions?
In order to approve a redesignation
from nonattainment to attainment,
section 107(d)(3)(E)(iii) of the CAA
requires EPA to determine that the
improvement in air quality is due to
emission reductions that are permanent
and enforceable, and that the
improvement results from the
implementation of the applicable SIP
and applicable federal air pollution
control regulations and other permanent
and enforceable regulations. Under this
criterion, a state must be able to
reasonably attribute the improvement in
air quality to emissions reductions that
are permanent and enforceable.
Attainment resulting from temporary
reductions in emission rates (e.g.,
reduced production or shutdown due to
temporary adverse economic
conditions) or unusually favorable
meteorology would not qualify as an air
quality improvement due to permanent
and enforceable emission reductions.
See Calcagni Memorandum at 4. In its
demonstration that improvements in air
quality are reasonably attributable to
emissions reductions that are permanent
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and enforceable, Montana evaluated
several factors: 26 the composition of
PM2.5 in the nonattainment area; control
measures that have been implemented
since the area was redesignated to
nonattainment; changes to the emissions
inventory over time; and meteorological
and economic trends. In its evaluation,
Montana identified two fugitive area
sources contributing to PM2.5
concentrations in the nonattainment
area: wood combustion and tailpipe
emissions. Eighty-two percent of the
PM2.5 concentrations during the baseline
study year of 2005 was attributed to
wood combustion. Wood combustion
impacts represented both residential
and small commercial space heating,
and outdoor burns. The State identified
emission reductions from only the wood
combustion category in the attainment
plan; the plan did not take credit for
reductions from mobile source tailpipe
emissions due to federal tailpipe
standards or fleet turnover.
In its approved Moderate
nonattainment plan, Montana adopted
permanent and enforceable rules from
the Lincoln County Air Pollution
Control Program. This program includes
rules that reduce PM2.5 impacts in the
nonattainment area resulting in
attainment of PM2.5 NAAQS.27 The air
pollution control rules in Chapter 1,
Subchapters 1 through 4 of the Lincoln
County Air Pollution Control Program,
address solid fuel burning devices, reentrained road dust control, and
outdoor burning regulations. These
rules are part of the Lincoln County
Health Department’s Health and
Environmental Rules in Chapter 1. The
rules contain the following subchapters,
all designed to help Lincoln County
attain the PM2.5 NAAQS:
• Subchapter 1—(75.1.100–106)—
General Provisions;
• Subchapter 2—(75.1.200–
206,208)—Solid Fuel Burning Device
Regulations;
• Subchapter 3—(75.1.301–308)—
Dust Control Regulations; and
• Subchapter 4—(75.1.401–408)—
Outdoor Burning Regulations.
The regulations in Lincoln County’s
Subchapter 2 require that solid fuel
burning devices be permitted by the
Lincoln County Environmental Health
Department. The regulations restrict the
material allowed for combustion and
prohibit visible emissions greater than
20 percent opacity. Lincoln County will
26 See Montana’s attainment plan for the Libby
Area, approved on March 17, 2011 (76 FR 14584).
27 See Section 1.3 in the Libby Area SIP
submission. Available in the docket for this
proposed rulemaking.
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call Air Pollution Alerts 28 when
particulate matter concentrations are
more than 80 percent of the 24-hour
standard and at that time, solid fuel
burning devices are not allowed to
operate unless the device has received
an exemption. A provision allows
exempt devices to be operated during an
alert, but only with an opacity of 10
percent or less.
Although re-entrained road dust is not
an identified emission source category,
Subchapter 3 of the Lincoln County
rules address re-entrained dust from
roads, parking lots and commercial lots
by requiring dust abatement and
control. These road dust regulations
apply within the regulated road sanding
and sweeping district as defined in the
regulation. Vehicular operations within
the district are only allowed on paved
surfaces within the district. To control
ice on the roads, liquid de-icing agents
and de-icing salts should be used.
Sanding material is not allowed unless
the Lincoln County Environmental
Health Department declares an
emergency and then only sanding
material that meets specific durability,
abrasion, and fine concentrations are
allowed. Roads are to be maintained
using a schedule of prioritized street
sweeping and flushing to remove carryon or applied materials. Commercial
operations shall also implement
measures to prevent depositing material
on yards/lots, suppress dust, and clean
adjoining roadways.
Lincoln County’s Subchapter 4
addresses outdoor burning and restricts
non-essential outdoor burning,
promoting alternative disposal methods
and recycling, and setting standards to
minimize emissions when outdoor
burning is necessary. These rules apply
to both the air pollution control district
which is the same area as the Libby
nonattainment area, and the Impact
Zone L, which extends beyond the
nonattainment area. The rules specify
which materials and activities are
prohibited for outdoor burning.
Residential outdoor burning is only
allowed in the month of April while
management burns are allowed from
April through October. Burning outside
these months requires additional
approval from the Lincoln County
Health Department. Burners must obtain
a burn permit from the Department and
may only conduct their burn if
meteorological conditions have good air
dispersion characteristics, as
determined by the Department.
Montana has determined that most of
the emissions reductions from the wood
28 See 75.1.206, Lincoln County Air Pollution
Control Program.
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combustion source category are
attributed to the Lincoln County
residential wood combustion rules.
These rules control residential and
small commercial wood combustion
used for space heating through a wood
stove permit program. The rules restrict
the installation and operation of wood
stoves to times with good air quality
dispersion. Lincoln County also has
outdoor open burning rules that require
burns to be permitted and approved to
ensure the burns occur during favorable
meteorological conditions.
Montana evaluated emissions from
residential wood burning contributing
to PM2.5 in Libby, Montana. Table 2.3 in
the June 24, 2020 Libby Area SIP
submission displays the 2005 actual
annual emissions, which are considered
the annual baseline emissions for Libby.
Additionally, the table shows the
annual emissions from the 2014
National Emissions Inventory (NEI). As
shown in the Table 2.3, emissions for
residential wood burning in 2014 have
decreased more than 85 percent
compared to the baseline emissions in
2005. The total emissions for area
source categories for 2014 total
emissions have decreased more than 62
percent compared to the 2005 baseline
emissions.
In addition, Montana has adopted
permitting requirements for major
stationary sources or major
modifications located in the
nonattainment areas including Libby,
Montana. They are located in the
Administrative Rules of Montana (ARM)
17.8.901 through 17.8.906. These rules
require all new sources or modifications
to use the lowest achievable emission
rate (LAER). Sources must obtain
emission reduction offsets in tons per
year (tpy) which provide a positive net
air quality benefit in the nonattainment
area using a one to one offset and must
be from the same source or another
emissions source within the same
nonattainment area. There must be
demonstrated improvement to the PM2.5
nonattainment with permanent,
quantifiable, and federally enforceable
reductions. A reduction of actual
emissions, not potential emissions, must
occur before a new source can be
permitted to operate.
In addition, Montana has a federally
enforceable permitting program for
minor sources in ARM, Title 17 Chapter
8, Subpart 7 that addresses PM2.5
emissions. These rules require sources
that emit 25 tpy or more of PM2.5 to
ensure the nonattainment area is not
negatively affected. Beginning in May
2019, Montana began requiring
registration of all sized asphalt plants,
concrete plants, mineral crushers, and
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mineral screens. The registration
program establishes conservative
operational restrictions on these
portable sources to prevent degradation
of the air quality in nonattainment areas
and elsewhere.
Not only has air quality in the Libby
Area benefited from the local district
and State rules discussed previously,
but the Area has also benefitted from
emission reductions from federal
measures including federal tailpipe
standards and the Federal Motor
Vehicle Control Program. Federal
tailpipe standards were designed to
reduce vehicle emissions, including
PM2.5. The previous control plan did not
take credit for the PM2.5 reductions
resulting from lower federal vehicle
emissions standards and vehicle fleet
turnover in the nonattainment area. The
federal tailpipe standards and vehicle
turnover will continue to reduce future
impacts and meet the requirements of
the 1990 CAA Amendments. The
Federal Motor Vehicle Control Program
controls tailpipe emissions and
evaporative emission standards for new
vehicles. Tailpipe impacts were less
than one percent of the Libby Area
during the 2005 baseline year.29 The
PM2.5 impact reductions are supported
by lower fleet vehicle fleet emissions as
fleet turnover continues.
Based upon the previously listed
actions by Montana in the submitted
maintenance plan, EPA finds that the
improvement in air quality in the Libby
Area is the result of permanent and
enforceable emissions reductions from a
combination of EPA-approved local and
State control measures and federal
control measures. As such, we believe
the criterion for redesignation set forth
in CAA section 107(d)(3)(E)(iii) is
satisfied.
C. Does the Area have a fully approved
maintenance plan pursuant to section
175A of the CAA?
For redesignating a nonattainment
area to attainment, the CAA requires
EPA to determine that the area has a
fully approved maintenance plan
pursuant to section 175A of the CAA
(CAA section 107(d)(3)(E)(iv)). In
conjunction with its request to
redesignate the Libby Area to attainment
for the 1997 annual PM2.5 NAAQS,
Montana submitted a SIP revision to
provide for the maintenance of the 1997
annual PM2.5 NAAQS for at least 10
years after the effective date of
redesignation to attainment. EPA
believes that this maintenance plan
29 See Table 2.3 in the Libby Area SIP submission.
Available in the docket for this proposed
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meets the requirements for approval
under section 175A of the CAA for the
reasons discussed in this section.
Section 175A of the CAA sets forth
the elements of a maintenance plan for
areas seeking redesignation from
nonattainment to attainment. Under
section 175A, the plan must
demonstrate continued attainment of
the applicable NAAQS for at least 10
years after the Administrator approves a
redesignation to attainment. Because the
1997 primary annual PM2.5 NAAQS will
be revoked for the Libby Area if it is
redesignated to attainment, Montana is
not required to submit a second 10-year
maintenance plan for the 1997 primary
annual PM2.5 NAAQS. See 81 FR 58010,
58144. To address the possibility of
future NAAQS violations, the
maintenance plan must contain such
contingency measures, as EPA deems
necessary, to assure prompt correction
of any future 1997 annual PM2.5 NAAQS
violations. The Calcagni Memorandum
provides further guidance on the
content of a maintenance plan,
explaining that a maintenance plan
should address five requirements: the
attainment emissions inventory;
maintenance demonstration;
monitoring; verification of continued
attainment; and a contingency plan. As
is discussed here, EPA finds that
Montana’s maintenance plan includes
all the necessary components and is
thus proposing to approve it as a
revision to the Montana SIP.
1. Attainment Emissions Inventory
As discussed previously, EPA is
proposing to determine that the Libby
Area is attaining the 1997 annual PM2.5
NAAQS based on a monitoring data for
the time period from 2014–2021.
Montana selected 2014 as the
attainment emission inventory year. The
attainment inventory identifies the level
of emissions in the Area that is
sufficient to attain the 1997 annual
PM2.5 NAAQS. Montana began
development of the attainment
inventory by first generating a baseline
emissions inventory for the Libby Area.
Montana selected 2005 as the base year
for developing a comprehensive
emissions inventory for direct PM2.5 and
the PM2.5 precursors SO2, NOX, VOCs,
and ammonia. See 76 FR 14584 (March
17, 2011). The Wegman Memorandum
states that an attainment inventory
should represent emissions during the
same 5-year period associated with the
air quality data used to determine that
the area meets the applicability
requirements of the LMP option. The
Libby LMP, provided in Montana’s June
24, 2020 SIP submission, includes an
emission inventory from 2014,
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representative of the 2014–2021 time
period which served as the 5-year
period relied upon in limited
maintenance plans as meeting the air
quality data requirements of the
Wegman Memorandum. 30
2. Maintenance Demonstration
Montana’s SIP submission for the
Libby Area employs the CDV method
laid out in the 2001 Wegman
Memorandum to demonstrate that the
Area is eligible for an LMP. As noted
previously, the CDV calculation from
the Wegman Memorandum represents
the highest design value an area could
have before it would violate the NAAQS
given a 1 in 10 probability—that is, if
the area’s current ADV (based on the
most recent five years of data) is less
than the CDV, there is a less than 1 in
10 probabilities that the area will violate
in the future. The State’s submission
calculates the ADV as 10.9 mg/m3 and
calculates the site-specific CDV as 14.1
mg/m3 using the Libby Area monitor
data from 2014–2018. Therefore, the
State’s submission showed the Libby
ADV is less than the CDV, but because
of the time that has elapsed since the
State’s submission, EPA has also
analyzed more recent data that are
available in AQS and have been
certified by the MDEQ.
To calculate the ADV we averaged the
most recent five design values for the
PM2.5 annual standard. Since each
design value is calculated by averaging
three years of valid annual means, the
average of the last five design values
includes data from the most recent 7year period (2014–2021). Table 3
presents the most recent annual PM2.5
NAAQS design values for 2017–2021
and presents the resulting ADV of 13.2
mg/m3.
To calculate the CDV we use the most
recent five years of design values and
their variability with the equation
presented in the Wegman Memorandum
(Table 3). The resulting site-specific
CDV is calculated to be 14.6 mg/m3
(Table 5). Therefore, the ADV (13.2 mg/
m3) falls below the site-specific CDV of
30 The emissions inventory included in the Libby
Area SIP submission is the 2014 NEI. The NEI is
a composite of data from many different sources,
with PM data coming primarily from EPA models
as well as from state, tribal, and local air quality
management agencies. Different data sources use
different data collection methods, and many of the
emissions data are based on estimates rather than
actual measurements. EPA considers the 2014 NEI
representative of the period from 2014–2021
because Montana provided comparable vehicle
miles traveled (VMT) data in their submission. See
Libby Area SIP submission, Appendix A, Montana
Department of Transportation Future VMT
Projections, p. A–1 in docket for this proposed
rulemaking.
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14.6 mg/m3 and thus meets the first
criterion for LMP eligibility.31
TABLE 3—ANNUAL PM2.5 NAAQS DESIGN VALUES (μg/m3) 32
2017 Design value
(2015–2017) *
2018 Design value
(2016–2018) *
2019 Design value
(2017–2019) *
2020 Design value
(2018–2020) *
2021 Design value
(2019–2021) *
Average of most
recent 3-year
design values (ADV)
13.0
12.9
13.4
13.3
13.3
13.2
TABLE 4—ELIGIBILITY CALCULATION EQUATIONS
Critical Design Value ................................................................................
Coefficient of Variation .............................................................................
Projected DV due to Motor Vehicle Growth over 10 years .....................
CDV = NAAQS/(1 + (tc × CV))
CV = s/ADV
Projected DV = ADV + (VMTpi × DVmv)]
ADV = Average of 3-year design values.
DV = Design value.
DVmv = motor vehicle design value based on on-road mobile portion of the attainment year inventory.
NAAQS = Applicable standard (15 μg/m3).
s = standard deviation of design values.
tc = Critical t-value (based on the one-tail student’s t-distribution, at a significance level of 0.10).
VMTpi = Projected percent increase in vehicle miles traveled (VMT) over the next 10 years.
TABLE 5—CALCULATION OF THE CDV USING 2017–2021 DESIGN VALUES
NAAQS .....................................................................................................
Tc ..............................................................................................................
ADV (2017–2021) .....................................................................................
S ................................................................................................................
CV .............................................................................................................
CDV = [NAAQS/(1 + tc × CV)] .................................................................
In addition to having an ADV that is
at or below the site-specific CDV, the
2001 Wegman Memorandum also
provides a methodology for calculating
a margin of safety factor based on
expected growth in mobile source
emissions. The memo lays out in
Attachment B a motor vehicle regional
emissions analysis test, which is
designed to account for an area’s
expected change in vehicle miles
traveled, to determine whether
increased emissions from on-road
mobile sources could, in the next 10
years, increase concentrations in the
area and threaten the assumption of
maintenance that underlies LMP policy.
15.0 μg/m3
1.533
13.2 μg/m3
0.2168 μg/m3
0.0164
14.6 μg/m3
In its June 24, 2020 SIP submission,
Montana employed the motor vehicle
regional emissions analysis test outlined
in Attachment B of the Wegman
Memorandum to demonstrate that the
Libby Area’s expected growth in mobile
source emissions would not threaten
maintenance of the NAAQS. Using data
from 2014–2018 the State calculated
that due to growth in mobile source
emissions the ADV may increase from
10.9 mg/m3 to 11.1 mg/m3 in the next 10
years, but that 11.1 mg/m3 is still below
the margin of safety as defined by the
site-specific CDV (14.1 mg/m3). EPA has
also examined more recent data to
confirm that even with updated
information, the test continues to show
that anticipated growth in mobile source
emissions should not interfere with the
Libby Area’s maintenance of the 1997
annual PM2.5 NAAQS. Using design
values from 2017–2021, we calculated
that due to expected growth in mobile
source emissions, the ADV may increase
from 13.2 mg/m3 to 13.5 mg/m3 in the
next 10 years, but that 13.5 mg/m3 is still
below the margin of safety as defined by
the site-specific CDV (14.6 mg/m3). For
the calculations used to determine how
the Libby Area passed the motor vehicle
regional analysis test, see Table 6.33
TABLE 6—MOTOR VEHICLE REGIONAL EMISSIONS ANALYSIS TEST CALCULATIONS
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ADV (2017–2021) .....................................................................................
VMTpi ........................................................................................................
DVmv .........................................................................................................
Calculated [ADV + (VMTpi × DVmv)] ........................................................
13.2 μg/m3
11.56%
2.5 μg/m3
13.5 μg/m3
The 2001 Wegman Memorandum also
indicates that once a state has an
approved LMP, the state will be
expected to determine, on an annual
basis, that the LMP criteria are still
being met. If the state determines that
the LMP criteria are not being met, it
should take action to reduce PM2.5
concentrations enough to requalify for
the LMP. One possible approach a state
could take is to implement contingency
measures. For a description of
contingency provisions included in the
Libby LMP, see section 3.6 of Montana’s
June 24, 2020 SIP submission.
Although the State flagged some PM2.5
values as potentially affected by
exceptional events, such as wildfire
31 See Libby PM
2.5 CDV Calculations in docket for
this proposed rulemaking.
32 In Table 3, (years)* is referring to what data
was included in the calculation for each 3-year
design value.
33 See Memo to File, Libby MT Motor Vehicle
Regional Emission Analysis in docket for this
proposed rulemaking.
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smoke, this action utilizes all qualityassured monitoring data from Libby. A
2019 memo from Richard Wayland and
Anna Wood regarding additional
methods, determinations, and analyses
to modify air quality data beyond
exceptional events,34 indicates that
monitoring data could qualify for
exclusion for use in calculating air
quality design values in support of a
NAAQS LMP submission and any
subsequent yearly design value
calculations for areas with approved
LMPs. The memorandum states that
such data exclusion requests will be
treated in a manner analogous to the
treatment of exceedance data under the
Exceptional Events Rule (EER). Since
the Libby Area qualifies for the LMP
option without the removal of any
demonstrated values, the flagged data
have no regulatory significance and
therefore the demonstrated values are
included in the calculations and remain
in AQS. Additional information on the
EER can be found in 40 CFR 50.14 and
40 CFR 51.930.
Pursuant to the Wegman
Memorandum, the State’s approved
maintenance plan should include an
emissions inventory (attainment
inventory) which can be used to
demonstrate attainment of the NAAQS.
The inventory should represent
emissions during the same 5-year period
associated with air quality data used to
determine whether the area meets the
applicability requirements of the LMP
option. The state should review its
inventory every three years to ensure
emissions growth is incorporated in the
attainment inventory, if necessary. In
this instance, Montana completed an
attainment year inventory for 2014 for
the Libby Area. EPA has reviewed the
2014 emissions inventories and
determined that they are appropriate for
this plan.
3. Monitoring Network
The PM2.5 monitoring network for the
Libby Area has been developed and
maintained in accordance with federal
siting and design criteria in 40 CFR part
58, appendices D and E and in
consultation with EPA Region 8. In
section 3.5 of the Libby LMP, located
within Montana’s June 24, 2020 SIP
submission, Montana states that it will
continue to operate its monitoring
network to meet EPA requirements at 40
CFR part 58 and identify any issues or
adjustments via the annual Ambient Air
34 See the memorandum from Richard Wayland,
Director of Air Quality Assessment Division and
Anna Marie Wood, Director of Air Quality Policy
Division, dated April 4, 2019, entitled, ‘‘Additional
Methods, Determinations, and Analyses to Modify
Air Quality Data Beyond Exceptional Events.’’
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Monitoring Network Plan or formal
communication. EPA approved
Montana’s 2021 monitoring plan on
November 16, 2021.35
4. Verification of Continued Attainment
Montana, through MDEQ, has the
legal authority to enforce and
implement the requirements of the
Libby LMP. This includes the authority
to adopt, implement, and enforce any
subsequent emissions control
contingency measures determined to be
necessary to correct future PM2.5
attainment problems.
In demonstrating maintenance,
continued attainment of the NAAQS can
be verified through operation of an
appropriate air quality monitoring
network. The Calcagni Memorandum
(p.11) states that the maintenance plan
should contain provisions for continued
operation of air quality monitors that
will provide such verification. As
discussed in section V of this document,
PM2.5 is currently monitored by MDEQ
within the Libby Area. In section 3.5 of
Montana’s submitted maintenance plan,
MDEQ intends to maintain an
appropriate PM2.5 monitoring network
and review monitoring and emissions
data through the maintenance period.
MDEQ will track the progress of the
maintenance plan by performing future
reviews of triennial emission
inventories for the Libby Area as
required in the Air Emissions Reporting
Rule (AERR). Emissions information
will be compared to the attainment year
to assure continued compliance with
the annual PM2.5 standard.
5. Contingency Provisions
Section 175A(d) of the CAA requires
that the maintenance plan contains
contingency provisions to assure that
the state will promptly correct any
violation of the relevant PM2.5 NAAQS
that may occur after the redesignation of
the area to attainment. Such provisions
must include a requirement that the
state will implement all measures with
respect to the control of the air pollutant
concerned that were contained in the
SIP for the area before redesignation of
the area as an attainment area. EPA’s
redesignation guidance notes that the
state is not required to have fully
adopted contingency measures that will
take effect without further action by the
state. As such, the contingency plan
should ensure that the state has the
capacity to adopt the contingency
measures expediently if the need were
triggered. Therefore, the primary
elements of this contingency plan
35 See MT AMNP Approval Letter 2021 in docket
for the proposed rulemaking.
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involve the tracking and triggering
mechanisms to determine when
contingency measures would be
necessary and a process for
implementing appropriate control
measures.
Montana will continue to monitor and
analyze PM2.5 concentrations to
determine continued maintenance of the
relevant PM2.5 NAAQS. In accordance
with 40 CFR part 58, MDEQ will
continue to operate the Libby monitor
(Site ID 30–053–0018).
If the State determines the Libby Area
has exceeded the 1997 annual PM2.5
NAAQS, the triggering of the
contingency plan does not automatically
require a revision of the SIP, nor is the
Area necessarily redesignated once
again to nonattainment. Instead, MDEQ
will have an appropriate timeframe to
correct the violation with
implementation of one or more adopted
contingency measures. If violations
continue to occur, additional
contingency measures may need to be
adopted until the violations are
corrected.
Montana has adopted a contingency
provision to address future PM2.5 air
quality problems. The contingency
provisions in the Libby PM2.5 LMP are
contained in section 3.6. of Montana’s
June 24, 2020, SIP submission. MDEQ
identifies the following steps if a
violation occurs, and the State triggers
the contingency plan:
1. Within 12 months of an exceedance
notification, MDEQ and the local
government in the Libby Area will
commence an analysis to review
information about historical
exceedances of the standard, the
meteorological conditions related to
recent exceedance(s), most recent
growth, and emissions, and if the
possibility of an exceptional event
occurred. MDEQ will develop
appropriate contingency measure(s) to
correct the violation of the PM2.5
standard.
2. Under the 2016 revisions to the
Treatment of Data Influenced by
Exceptional Events Rule (81 FR 68216),
MDEQ will confer with EPA Region 8
regarding whether any flagged
exceptional events would meet the
criteria of a regulatory decision, and if
so, a determination would be made on
whether to move forward with
producing a demonstration and if that
would trigger contingency measures.
3. If MDEQ and the local government
in the Libby Area finds locally adopted
control measures to be inadequate,
MDEQ and the local government will
adopt state-enforceable measures as
deemed necessary by MDEQ to prevent
additional exceedances or violations.
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Measures to be considered include
implementation of Libby’s Contingency
Rules 75.1.208 and 75.1.307, as spelled
out in Montana’s Libby PM2.5 attainment
plan, the use of deciphers, additional
street cleaning, etc.
Upon our review, we find that the
contingency provisions of the Libby
PM2.5 LMP satisfy the pertinent
requirements of section 175A of the
CAA.
D. Transportation and General
Conformity
The requirements for transportation
and general conformity are found in
CAA section 176(c). Conformity to the
SIP means that transportation-related
actions (transportation conformity) and
other federal actions (general
conformity) will not cause or contribute
to any new violation of any standard in
any area, increase the frequency or
severity of any existing violation of any
standard in any area or delay timely
attainment of any standard or any
required interim emission reductions or
other milestones in any area (CAA
section 176(c)(1)(B)).
As discussed in section II.B, if the
proposal is finalized, the 1997 primary
annual PM2.5 NAAQS will be revoked in
the Libby Area on the effective date of
the redesignation. Beginning on that
date, the Area will no longer be subject
to transportation conformity or general
conformity requirements for the 1997
annual PM2.5 NAAQS due to the
revocation of the 1997 primary annual
PM2.5 NAAQS. See 81 FR 58125–6.
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V. What are the effects of EPA’s
proposed actions?
EPA’s proposed actions establish the
basis upon which EPA may take final
action on the issues being proposed for
approval. Approval of Montana’s
redesignation request would change the
legal designation of Lincoln County for
the 1997 annual PM2.5 NAAQS, found at
40 CFR part 81, from nonattainment to
attainment. The limited maintenance
plan includes contingency measures to
remedy any future violations of the 1997
annual PM2.5 NAAQS and procedures
for evaluation of potential violations.
VI. Proposed Actions
EPA is proposing to: (1) determine
that the Libby Area is attaining the 1997
annual PM2.5 NAAQS based on 2014–
2021 data; (2) approve Montana’s plan
for maintaining the 1997 annual PM2.5
NAAQS (limited maintenance plan);
and (3) redesignate the Libby Area to
attainment for the 1997 annual PM2.5
NAAQS. If finalized, approval of the
redesignation request would change the
official designation of Lincoln County
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for the 1997 annual PM2.5 NAAQS,
found at 40 CFR part 81 from
nonattainment to attainment, as found
at 40 CFR part 81.
VII. Statutory and Executive Order
Reviews
Under the CAA, redesignation of an
area to attainment and the
accompanying approval of a
maintenance plan are actions that affect
the status of a geographical area and do
not impose any additional regulatory
requirements on sources beyond those
imposed by state law. A redesignation to
attainment does not in and of itself
create any new requirements, but rather
results in the applicability of
requirements contained in the CAA for
areas that have been redesignated to
attainment. Moreover, the Administrator
is required to approve a SIP submission
that complies with the provisions of the
Act and applicable federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely proposes to approve state law as
meeting federal requirements and does
not impose additional requirements
beyond those imposed by state law. For
these reasons, this proposed action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Public Law 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
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application of those requirements would
be inconsistent with the CAA; and
• Executive Order 12898 (59 FR 7629,
February 16, 1994, 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 program,
policies, and activities on minority
populations (people of color/Indigenous
people) and low-income populations.
In addition, the SIP is not approved
to apply on any Indian reservation land
or in any other area where EPA or an
Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, the proposed rule does
not have tribal implications and will not
impose substantial direct costs on tribal
governments or preempt tribal law as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000).
List of Subjects
40 CFR Part 52
Environmental protection, Air
pollution control, Carbon monoxide,
Greenhouse gases, Incorporation by
reference, Intergovernmental relations,
Lead, Nitrogen dioxide, Ozone,
Particulate matter, Reporting and
recordkeeping requirements, Sulfur
oxides, Volatile organic compounds.
40 CFR Part 81
Environmental protection, Air
pollution control, National parks, and
Wilderness areas.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 1, 2022.
KC Becker,
Regional Administrator, Region 8.
[FR Doc. 2022–26504 Filed 12–5–22; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 622
[Docket No. 221130–0256]
RIN 0648–BL29
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic; Reef Fish
Fishery of the Gulf of Mexico;
Vermilion Snapper Harvest Levels
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
AGENCY:
E:\FR\FM\06DEP1.SGM
06DEP1
Agencies
[Federal Register Volume 87, Number 233 (Tuesday, December 6, 2022)]
[Proposed Rules]
[Pages 74577-74588]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2022-26504]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[EPA-R08-OAR-2021-0003; FRL-10454-01-R8]
Approval and Promulgation of Implementation Plans; Montana; Libby
1997 Annual PM2.5 Limited Maintenance Plan and Redesignation Request
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
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SUMMARY: The Environmental Protection Agency (EPA or the Agency) is
proposing to take three separate but related actions. First, EPA is
proposing to determine that the Libby fine particulate matter
(PM2.5) nonattainment area (Libby Area) is attaining the
1997 annual PM2.5 national ambient air quality standards
(NAAQS or standard) based on 2014-2021 data. The Agency is also
proposing to approve Montana's plan for maintaining the 1997 annual
PM2.5 NAAQS (limited maintenance plan) and to redesignate
the Libby Area to attainment for the 1997 annual PM2.5
NAAQS, submitted by the State of Montana on June 24, 2020.
DATES: Written comments must be received on or before January 5, 2023.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R08-
OAR-2021-0003, to the Federal Rulemaking Portal at https://www.regulations.gov. Follow the online instructions for submitting
comments. Once submitted, comments cannot be edited or removed from
www.regulations.gov. EPA may publish any comment received to its public
docket. Do not submit electronically any information you consider to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Multimedia submissions (audio,
video, etc.) must be accompanied by a written comment. The written
comment is considered the official comment and should include
discussion of all points you wish to make. EPA will generally not
consider comments or comment contents located outside of the primary
submission (i.e., on the web, cloud, or other file sharing system). For
additional submission methods, the full EPA public comment policy,
information about CBI or multimedia submissions, and general guidance
on making effective comments, please visit https://www2.epa.gov/dockets/commenting-epa-dockets.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available electronically in
www.regulations.gov. To reduce the risk of COVID-19 transmission, for
this action we do not plan to offer hard copy review of the docket.
Please email or call the person listed in the FOR FURTHER INFORMATION
CONTACT section if you need to make alternative arrangements for access
to the docket.
FOR FURTHER INFORMATION CONTACT: Amrita Singh, Air and Radiation
Division, U.S. Environmental Protection Agency (EPA), Region 8, Mail
Code ARD-QP, 1595 Wynkoop Street, Denver, Colorado 80202-1129,
telephone number: (303) 312-6103, email address: [email protected].
SUPPLEMENTARY INFORMATION: Throughout this document wherever ``we,''
``us,'' or ``our'' is used, we mean EPA.
Table of Contents
I. What are the actions EPA is proposing to take?
[[Page 74578]]
II. What is the background for EPA's proposed actions?
A. The PM2.5 NAAQS
B. Designation of PM2.5 NAAQS Nonattainment Areas
C. PM2.5 NAAQS Nonattainment Area Planning
Requirements
D. Limited Maintenance Plans
III. Why is EPA proposing these actions?
IV. What is EPA's analysis of the request?
A. Has the State met all applicable requirements under section
110 and part D of the Clean Air Act (CAA) and have those
requirements been fully approved? (CAA sections 107(d)(3)(E)(ii) and
(v))
B. Has the State demonstrated that air quality improvement is
due to permanent and enforceable reductions?
C. Does the area have a fully approved maintenance plan pursuant
to section 175A of the CAA?
D. Transportation and General Conformity
V. What are the effects of EPA's proposed actions?
VI. Proposed Actions
VII. Statutory and Executive Order Reviews
I. What are the actions EPA is proposing to take?
EPA is proposing to take the following separate but related
actions: (1) to determine that the Libby Area is attaining the 1997
annual PM2.5 NAAQS based on 2014-2021 data; (2) to approve
Montana's plan for maintaining the 1997 annual PM2.5 NAAQS
(limited maintenance plan); and (3) to redesignate the Libby Area to
attainment for the 1997 annual PM2.5 NAAQS.
Libby, Montana is a small rural community located in Lincoln County
in the northwestern part of the State. Libby sits in the narrow,
triangular Kootenai valley at an elevation of 2,100 feet. The Libby
Area is dominated by three major mountain ranges that limit the air-
shed: (1) the Rocky Mountain and Flathead Ranges on the eastern
boundary; (2) the Purcell Range, which roughly bisects the area from
north to south; and (3) the Selkirk and Cabinet Ranges on the western
boundary. Most of the area surrounding Libby, Montana is national
forest land managed by the U.S. Forest Service.
These proposed actions are summarized and described in greater
detail throughout this proposed rulemaking. EPA's 1997 annual
PM2.5 nonattainment designation for the Libby Area triggered
an obligation for Montana to develop a nonattainment state
implementation plan (SIP) revision addressing certain Clean Air Act
(CAA) requirements under title I, part D, subpart 1 (hereinafter
``Subpart 1'') and title I, part D, subpart 4 (hereinafter ``Subpart
4''). Subpart 1 contains the general requirements for nonattainment
areas for criteria pollutants, including requirements to develop a SIP
that provides for the implementation of reasonably available control
measures (RACM) under section 172(c)(1), reasonable further progress
(RFP), includes base-year and attainment-year emissions inventories,
and for the implementation of contingency measures. As discussed in
greater detail later in this document, Subpart 4 contains specific
planning and scheduling requirements for coarse particulate matter
(PM10) nonattainment areas, including requirements for new
source review (NSR), RACM (under CAA section 189(a)(1)(C)), and RFP.
EPA's longstanding general guidance interpreting the 1990 CAA
Amendments, known as the General Preamble, EPA discussed the
relationship of Subpart 1 and Subpart 4 SIP requirements and pointed
out that Subpart 1 requirements were to an extent ``subsumed by, or
integrally related to, the more specific PM-10 requirements.'' See 57
FR 13538 (April 16, 1992). In addition, under the United States Court
of Appeals for the District of Columbia Circuit's (D.C. Circuit's)
January 4, 2013, decision in Natural Resources Defense Council (NRDC)
v. EPA, 706 F.3d 428 (D.C. Cir. 2013), Subpart 4 requirements apply to
PM2.5 nonattainment areas.\1\
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\1\ In explaining its decision, the Court reasoned that the
plain meaning of the CAA requires implementation of the 1997
PM2.5 NAAQS under Subpart 4 because PM2.5
particles fall within the statutory definition of PM10
and are thus subject to the same statutory requirements. EPA
finalized its interpretation of Subpart 4 requirements as applied to
the PM2.5 NAAQS in its final rule entitled ``Fine
Particulate Matter National Ambient Air Quality Standards: State
Implementation Plan Requirements; Final Rule'' (81 FR 58010, August
24, 2016).
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On June 2, 2014 (79 FR 31566), EPA published a rule entitled
``Identification of Nonattainment Classification and Deadlines for
Submission of State Implementation Plan (SIP) Provisions for the 1997
Fine Particle (PM2.5) National Ambient Air Quality Standard
(NAAQS) and 2006 PM2.5 NAAQS'' (``Classification and
Deadlines Rule''). In that rule, the Agency responded to the D.C.
Circuit's January 2013 decision by identifying all PM2.5
nonattainment areas for the 1997 and 2006 PM2.5 NAAQS as
``Moderate'' nonattainment areas under Subpart 4, and by establishing a
new SIP submission date of December 31, 2014, for Moderate area
attainment plans and for any additional attainment-related or
nonattainment new source review plans necessary for areas to comply
with the requirements applicable under Subpart 4. Id. at 31567-70.
EPA is proposing to determine that the Libby Area is attaining the
1997 annual PM2.5 NAAQS based on recent air quality data.
EPA is also proposing to approve Montana's limited maintenance plan
(LMP) for the Libby Area as meeting the requirements of section 175A of
the CAA.
EPA also proposes to determine that the Libby Area has met the
requirements for redesignation under section 107(d)(3)(E) of the CAA.
This proposed rulemaking is in response to Montana's June 24, 2020
redesignation request and associated SIP submission that address the
requirements described in section 107(d)(3)(E) of the CAA for the
redesignation of the Libby Area from nonattainment to attainment for
the 1997 annual PM2.5 NAAQS.\2\
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\2\ See Libby Area SIP submission, available in the docket for
this proposed rulemaking.
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II. What is the background for EPA's proposed actions?
A. The PM2.5 NAAQS
Particulate matter includes particles with diameters that are
generally 2.5 microns or smaller (PM2.5) and particles with
diameters that are generally 10 microns or smaller (PM10).
PM2.5 contributes to effects that are harmful to human
health and the environment, including premature mortality, aggravation
of respiratory and cardiovascular disease, decreased lung function,
visibility impairment, and damage to vegetation and ecosystems.
Individuals particularly sensitive to PM2.5 exposure include
older adults, people with heart and lung disease, and children. See 78
FR 3086 at 3088 (January 15, 2013). PM2.5 can be emitted
directly into the atmosphere as a solid or liquid particle (``primary
PM2.5'' or ``direct PM2.5'') or can be formed in
the atmosphere (``secondary PM2.5'') as a result of various
chemical reactions among precursor pollutants such as nitrogen oxides
(NOX), sulfur oxides (SOX), volatile organic
compounds (VOCs), and ammonia (NH3).\3\
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\3\ EPA, Air Quality Criteria for Particulate Matter, No. EPA/
600/P-99/002aF and EPA/600/P-99/002bF, October 2004.
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Under section 109 of the CAA, EPA has established national ambient
air quality standards for certain pervasive air pollutants (referred to
as ``criteria pollutants'') and conducts periodic reviews of the NAAQS
to determine whether they should be revised or whether new NAAQS should
be established. EPA sets the NAAQS for criteria pollutants at levels
required to protect public health and welfare.\4\
[[Page 74579]]
PM2.5 is one of the ambient pollutants for which EPA has
established health-based standards.
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\4\ For a given air pollutant, ``primary'' national ambient air
quality standards are those determined by EPA as requisite to
protect the public health. ``Secondary'' standards are those
determined by EPA as requisite to protect the public welfare from
any known or anticipated adverse effects associated with the
presence of such air pollutant in the ambient air. CAA section
109(b).
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On July 18, 1997 (62 FR 38652), EPA revised the NAAQS for
particulate matter to add new standards for PM2.5. The
Agency established primary and secondary annual and 24-hour standards
for PM2.5. The annual standard was set at 15.0 micrograms
per meter cubed ([micro]g/m\3\) based on a 3-year average of annual
mean PM2.5 concentrations, and the 24-hour (daily) standard
was set at 65 [micro]g/m\3\ based on the 3-year average of the annual
98th percentile values of 24-hour PM2.5 concentrations at
each population-oriented monitor within an area.\5\
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\5\ The primary and secondary standards were set at the same
level for both the 24-hour and the annual PM2.5
standards.
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On October 17, 2006 (71 FR 61144), EPA retained the annual average
NAAQS at 15.0 [micro]g/m\3\ but revised the level of the 24-hour
PM2.5 NAAQS to 35 [micro]g/m\3\ based on a 3-year average of
the annual 98th percentile values of 24-hour concentrations.\6\
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\6\ Under EPA regulations at 40 CFR part 50, the primary and
secondary 2006 24-hour PM2.5 NAAQS are attained when the
annual arithmetic mean concentration, as determined in accordance
with 40 CFR part 50, appendix N, is less than or equal to 35
[micro]g/m\3\ at all relevant monitoring sites in the subject area,
averaged over a 3-year period.
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On December 14, 2012, EPA promulgated the 2012 PM2.5
NAAQS, including a revision of the annual standard to 12.0 [micro]g/
m\3\ based on a 3-year average of annual mean PM2.5
concentrations. The Agency maintained the 24-hour standard of 35
[micro]g/m\3\ based on a 3-year average of the 98th percentile of 24-
hour concentrations. See 78 FR 3086 (January 15, 2013).
B. Designation of PM2.5 NAAQS Nonattainment Areas
Following promulgation of a new or revised NAAQS, EPA is required
by CAA section 107(d) to designate areas throughout the nation as
attaining or not attaining the NAAQS. On January 5, 2005 (70 FR 944),
EPA published area designations for the 1997 PM2.5 NAAQS
based on air quality data for the calendar years 2001-2003. In that
rulemaking, EPA designated Libby, Montana as nonattainment for the 1997
annual PM2.5 NAAQS. These designations became effective on
April 5, 2005.
On March 17, 2011 (76 FR 14584), EPA approved Montana's attainment
plan which included an attainment demonstration, an analysis of
reasonable available control technology/reasonable available control
measure (RACT/RACM), base-year and projection year inventories, and
contingency measures for the 1997 PM2.5 NAAQS for the Libby
Area. On July 14, 2015 (80 FR 40911), EPA finalized its determination
that the Libby Area attained the 1997 annual PM2.5 NAAQS by
the Area's statutory attainment date of December 31, 2011. This
determination was based upon quality-assured and certified ambient air
monitoring data for the 2007-2009 monitoring period that demonstrated
that the Libby Area attained the 1997 annual PM2.5 NAAQS by
the attainment date. In the same rulemaking, EPA also issued a clean
data determination under the Agency's Clean Data Policy \7\ based upon
quality-assured and certified ambient air monitoring data that
demonstrated the Libby Area continued to attain the 1997 annual
PM2.5 NAAQS based on 2012-2014 monitoring data.\8\
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\7\ See e.g., 70 FR 71612 (November 29, 2005) and 72 FR 20586
(April 25, 2007).
\8\ See 71 FR 19935 (April 14, 2015) that addresses the final
clean data determination and a final determination of attainment by
the attainment date for the Libby nonattainment area. As part of its
clean data determination submission to EPA, Montana submitted the
clean data determination to address the national ambient air
requirements under Subpart 4.
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On July 29, 2016, EPA issued a rule entitled ``Fine Particulate
Matter National Ambient Air Quality Standards: State Implementation
Plan Requirements'' (``PM2.5 SIP Requirements Rule''). See
81 FR 58010 (August 24, 2016). This rule clarifies how states should
meet the statutory SIP requirements that apply to areas designated
nonattainment for any PM2.5 NAAQS under Subparts 1 and 4. It
does so by establishing regulatory requirements and by providing
guidance that is applicable to areas that are currently designated
nonattainment for existing PM2.5 NAAQS and areas that are
designated nonattainment for any PM2.5 NAAQS in the future.
In addition, the rule responds to the D.C. Circuit's remand of the 1997
PM2.5 Implementation Rules. As a result, the requirements of
the rule also govern future actions associated with states' ongoing
implementation efforts for the 1997 and 2006 PM2.5 NAAQS. In
the PM2.5 SIP Requirements Rule, EPA revoked the 1997
primary annual PM2.5 NAAQS in areas that had always been
attainment for that NAAQS, and in areas that had been designated as
nonattainment but that were redesignated to attainment before October
24, 2016, the PM2.5 SIP Requirements Rule effective date.
See 81 FR 58010 (August 24, 2016).
In the August 24, 2016 final rule, EPA also finalized a provision
to revoke the 1997 primary annual PM2.5 NAAQS in areas
redesignated to attainment after October 24, 2016, on the effective
date of an area's redesignation. See 40 CFR 50.13(d). If this proposal
is finalized, the 1997 primary annual PM2.5 NAAQS will be
revoked for the Libby Area on the effective date of the redesignation.
Beginning on that date, the Area will no longer be subject to
transportation or general conformity requirements for the 1997 annual
PM2.5 NAAQS due to revocation of the primary NAAQS. See 81
FR 58125-6. If redesignated, the Libby Area will be required to
implement the maintenance plan requirements under section 175A for the
1997 annual PM2.5 NAAQS, and the prevention of significant
deterioration (PSD) program for the 1997 annual PM2.5 NAAQS.
Once approved, the maintenance plan can only be revised if the revision
meets the requirements of CAA section 110(l) and, if applicable, CAA
section 193. As described in the PM2.5 SIP Requirements
Rule, those 1997 annual PM2.5 maintenance areas with a
revoked NAAQS are no longer required to submit a second 10-year
maintenance plan for the 1997 annual PM2.5 NAAQS. See 81 FR
58144.
C. PM2.5 NAAQS Nonattainment Area Planning Requirements
The CAA establishes the requirements for redesignation of an area
from nonattainment to attainment. Specifically, section 107(d)(3)(E)
allows for redesignation of areas from nonattainment to attainment
provided that the following criteria are met:
(1) The Administrator has determined that the area has attained the
applicable NAAQS;
(2) The Administrator has fully approved the applicable SIP for the
area under section 110(k) of the CAA;
(3) The Administrator has determined that the improvement in air
quality is due to permanent and enforceable reductions in emissions;
(4) The Administrator has fully approved a maintenance plan for the
area as meeting the requirements of section 175A of the CAA; and
(5) The state containing the area has met all requirements
applicable to the area under section 110 and part D of the CAA.
Section 110 of the CAA identifies a comprehensive list of elements
that SIPs must include, and part D establishes the SIP requirements for
nonattainment areas. The generally applicable nonattainment SIP
requirements are found in part D, subpart 1, and the particulate
matter-specific SIP
[[Page 74580]]
requirements are found in part D, subpart 4.
On April 16, 1992 (57 FR 13498), EPA provided guidance on
redesignation in the General Preamble for the Implementation of Title I
of the CAA Amendments of 1990, and the Agency supplemented this
guidance on April 28, 1992 (57 FR 18070). EPA has provided further
guidance on processing redesignation requests in the following
documents:
1. ``Procedures for Processing Requests to Redesignate Areas to
Attainment,'' Memorandum from John Calcagni, Director, Air Quality
Management Division, September 4, 1992 (hereinafter referred to as
the ``Calcagni Memorandum'');
2. ``State Implementation Plan (SIP) Actions Submitted in
Response to Clean Air Act (CAA) Deadlines,'' Memorandum from John
Calcagni, Director, Air Quality Management Division, October 28,
1992; and
3. ``Part D New Source Review (Part D NSR) Requirements for
Areas Requesting Redesignation to Attainment,'' Memorandum from Mary
D. Nichols, Assistant Administrator for Air and Radiation, October
14, 1994 (hereinafter referred to as the ``Nichols Memorandum'').
D. Limited Maintenance Plans
CAA section 175A(a) requires that nonattainment areas seeking
redesignation to attainment submit ``a revision of the applicable state
implementation plan to provide for the maintenance of the [NAAQS] for
such air pollutant in the area concerned for at least 10 years after
the redesignation.'' EPA explained in the Calcagni Memorandum that
states may meet this requirement to ``provide for the maintenance of
the NAAQS'' by using projected emissions inventories or air quality
modeling showing continued maintenance until the end of the relevant
maintenance period. See Calcagni Memorandum at 9-11. EPA clarified in
three subsequent guidance memos that certain areas could meet the CAA
section 175A requirement to provide for maintenance by demonstrating
that the area's design value was well below the NAAQS and that the
historical stability of the area's air quality levels showed that the
area was unlikely to violate the NAAQS in the future.\9\ The Agency
refers to this streamlined demonstration of maintenance as a limited
maintenance plan.
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\9\ See ``Limited Maintenance Plan Option for Nonclassifiable
Ozone Nonattainment Areas'' from Sally L. Shaver, Office of Air
Quality Planning and Standards (OAQPS), dated November 16, 1994;
``Limited Maintenance Plan Option for Nonclassifiable CO
Nonattainment Areas'' from Joseph Paisie, OAQPS, dated October 6,
1995; Copies of these guidance memoranda can be found in the docket
for this proposed rulemaking.
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EPA has interpreted CAA section 175A as permitting this option
because section 175A does not define how areas may demonstrate
maintenance, and in EPA's experience with implementing the various
NAAQS, areas that qualify for an LMP and have approved LMPs, have
rarely, if ever, experienced subsequent violations of the NAAQS. As
noted in the LMP guidance memoranda, states seeking an LMP must still
submit the other maintenance plan elements outlined in the Calcagni
Memorandum, including an attainment emissions inventory, provisions for
the continued operation of the ambient air quality monitoring network,
verification of continued attainment, and a contingency plan in the
event of a future violation of the NAAQS. Moreover, states seeking to
do an LMP must still submit a CAA section 175A maintenance plan as a
revision to the SIP, with all attendant notice and comment procedures.
While the LMP guidance memoranda were originally written with respect
to certain NAAQS,\10\ EPA has extended the LMP interpretation of
section 175A to other NAAQS and pollutants not specifically covered by
the previous guidance memos.\11\
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\10\ The prior memos addressed unclassifiable areas under the 1-
hour ozone NAAQS, nonattainment areas for the PM10 NAAQS,
and nonattainment areas for the carbon monoxide NAAQS.
\11\ See, e.g., 79 FR 41900 (July 18, 2014) (approval of second
ten-year LMP for Grant County 1971 sulfur dioxide maintenance area).
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To determine the LMP eligibility criteria for the Libby Area, EPA
is interpreting the requirements as described in the 2001 memorandum
from Lydia Wegman \12\ regarding LMPs for PM10 areas as
applying to PM2.5. This memorandum states that one way for a
PM10 area to qualify for an LMP is to show that the area's
average design value (ADV) (based upon the most recent 5 years of
monitoring data) is at or below the critical design value (CDV). The
memorandum defines the CDV as an indicator of the likelihood of future
violations of the NAAQS in an area given the area's current ADV and its
historical variability and provides a means for calculating the CDV for
an area (or monitoring site) (Attachment A of the 2001 Wegman
Memorandum). The CDV is the highest average design value an area could
have before it may experience a future violation of the NAAQS with a
certain probability--in the case of the Wegman Memorandum, a
probability of 1 in 10. Therefore, if an area's current ADV is less
than the area's CDV, that area has a less than 1 in 10 chances of
violating the NAAQS in the future. As noted in Attachment A of the
Wegman Memorandum, the CDV calculation was designed to apply for any
NAAQS pollutant and is not specific to PM10. Montana
employed this methodology to demonstrate that the Libby Area is
eligible for an LMP and that the plan therefore provides for
maintenance of the NAAQS for 10 years following redesignation. We agree
that the State's demonstration meets the requirements of CAA section
175A and shows that the Area will continue to maintain the annual
PM2.5 NAAQS following redesignation through 2031. In its SIP
submission, Montana used a site-specific CDV calculated with
PM2.5 data from the one ambient design value monitor in the
Libby Area.
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\12\ ``Limited Maintenance Plan Option for Moderate
PM10 Nonattainment Areas'' from Lydia Wegman, OAQPS,
dated August 9, 2001 (hereinafter referred to as the ``Wegman
Memorandum''). A copy of this guidance memorandum can be found in
the docket for this proposed rulemaking.
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The 2001 Wegman Memorandum also provided that an LMP was
appropriate only for those PM10 areas that were expecting
limited growth of on-road motor vehicle emissions (including fugitive
dust), and therefore included a motor vehicle regional emissions
analysis demonstration that states seeking a PM10 LMP should
perform (Attachment B to the Wegman Memorandum). According to the
Wegman Memorandum, the demonstration should show that the ADV remains
below the margin of safety provided for in the memorandum, even after
the growth of on-road motor vehicle emissions is considered. This
proposed rulemaking uses the site-specific CDV instead of the margin of
safety described in the Wegman Memorandum for this analysis as EPA has
not recommended a margin of safety for the 1997 annual PM2.5
NAAQS.
III. Why is EPA proposing these actions?
On June 24, 2020, the State of Montana requested that EPA
redesignate the Libby Area to attainment for the 1997 annual
PM2.5 NAAQS and submitted an associated SIP revision
containing an LMP. EPA's evaluation of the plan and air quality data
indicates that the Libby Area meets the requirements for redesignation
set forth in section 107(d)(3)(E) of the CAA, including that the LMP
fulfills the maintenance plan requirements under section 175A of the
CAA. As a result of these findings, EPA is proposing to take the
separate but related actions to approve the LMP and redesignate the
[[Page 74581]]
Libby Area from nonattainment to attainment.
IV. What is EPA's analysis of the request?
To redesignate an area from nonattainment to attainment, the CAA
requires EPA to determine that the area has attained the applicable
NAAQS (CAA section 107(d)(3)(E)(i)). The criteria for determining if an
area is attaining the 1997 annual PM2.5 NAAQS is set out in
40 CFR 50.13 and 40 CFR part 50, appendix N. The 1997 annual
PM2.5 primary and secondary standards are met when the
annual design value \13\ at each eligible monitoring site within the
area is less than or equal to 15.0 [micro]g/m\3\.
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\13\ The Annual PM2.5 NAAQS design value is the 3-
year average of PM2.5 annual mean mass concentrations.
These annual means are calculated as the weighted arithmetic mean of
the four quarters of valid data at the site and the annual means are
only considered valid when they meet data completeness requirements
detailed in 40 CFR 50.13. Once three valid annual means are
available, they can be averaged together to determine the annual
design value for that site.
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Based on data from 2007-2009, EPA determined that the Libby Area
attained the 1997 annual PM2.5 standard by December 31,
2011, well before its attainment date of July 14, 2015.\14\ In
addition, EPA issued a final clean data determination under the Clean
Data Policy that the Libby Area was attaining the 1997 annual
PM2.5 NAAQS, based on quality-assured and certified ambient
air quality data for the 2012-2014 monitoring period. The Libby Area
has continued to attain the 1997 annual PM2.5 NAAQS since
EPA's earlier determinations that the Area attained the NAAQS.
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\14\ See 80 FR 40911.
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The Libby Area has one State and Local Air Monitoring Station
(SLAMS) monitor operated by the Montana Department of Environmental
Quality (MDEQ). This monitor (Air Quality System (AQS) Site ID 30-53-
0018) has complete data for 2014-2021, which is the period of data
utilized for this proposed redesignation.\15\
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\15\ The criteria for determining if an area is attaining the
1997 Annual PM2.5 NAAQS are set out in the 40 CFR 50.13
and 40 CFR part 50, appendix N. Three years of valid annual means
are required to produce a valid annual standard design value. A year
meets data completeness requirements when at least 75 percent of the
scheduled sampling days for each quarter have valid data.
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Table 1 summarizes the annual mean PM2.5 data collected
from 2014-2021 for the Libby Area.\16\ Table 2 shows the annual design
values for 2016-2021. The data presented in the tables were calculated
from all data available in AQS, including those data flagged by the
State of Montana as potentially influenced by exceptional events. EPA
deems these data valid as they are complete and have been certified by
MDEQ.
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\16\ The annual averages in Table 1 are calculated by averaging
the four quarters of data.
\17\ Annual mean concentration is the averaging of four complete
quarters of data for each year. See 40 CFR part 50, appendix N.
\18\ The Annual PM2.5 NAAQS design value is the 3-
year average of PM2.5 annual mean mass concentrations.
See 40 CFR 50.13.
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None of the annual design values from 2016-2021 from the Libby Area
monitoring site exceed the 1997 annual PM2.5 NAAQS of 15.0
[micro]g/m\3\, and as such, EPA proposes to determine that the Libby
Area has attained the 1997 annual PM2.5 NAAQS, and therefore
meets the requirement of CAA section 107(d)(3)(E)(i).
Table 1--PM2.5 One-Year Annual Mean Concentrations \17\
----------------------------------------------------------------------------------------------------------------
Year: 2014 2015 2016 2017 2018 2019 2020 2021
----------------------------------------------------------------------------------------------------------------
Concentration ([micro]g/m\3\)... 9.3 14.9 9.8 14.3 14.6 11.4 13.8 14.6
----------------------------------------------------------------------------------------------------------------
Table 2--PM2.5 Annual Design Value \18\
----------------------------------------------------------------------------------------------------------------
3-Year Period: 2014-2016 2015-2017 2016-2018 2017-2019 2018-2020 2019-2021
----------------------------------------------------------------------------------------------------------------
Design Value ([micro]g/m\3\) 11.4 13.0 12.9 13.4 13.3 13.3
----------------------------------------------------------------------------------------------------------------
A. Has the State met all applicable requirements under section 110 and
part D of the Clean Air Act (CAA) and have those requirements been
fully approved? (CAA sections 107(d)(3)(E)(ii) and (v))
Sections 107 (d)(3)(E)(ii) and (v) require EPA to determine that
the area has a fully approved applicable SIP under section 110(k) that
meets all the basic applicable requirements under section 110 and part
D for purposes for redesignation. The following is a summary of how
Montana meets these requirements.
1. CAA Section 110 Requirements
Section 110(a)(2) of title I of the CAA delineates the general
requirements for a SIP, which include enforceable emissions limitations
and other control measures, means or techniques, provisions for the
establishment and operation of appropriate devices necessary to collect
data on ambient air quality, and programs to enforce limitations. The
general SIP elements and requirements set forth in CAA section
110(a)(2) include, but are not limited to the following:
Submittal of a SIP that has been adopted by the state
after reasonable public notice and hearing;
Provisions for establishment and operation of appropriate
procedures needed to monitor ambient air quality;
Implementation of a source permit program;
Provisions for the implementation of part C requirements
(PSD);
Provisions for the implementation of part D requirements
for NSR permit programs;
Provisions for air pollution modeling; and
Provisions for public and local air agency participation
in planning and emission control rule development.
CAA section 110(a)(2)(D) requires that SIPs contain certain
measures to prevent sources in a state from significantly contributing
to air quality problems in another state; the portion of a state's SIP
that include these measures is known as an interstate transport SIP.
However, these CAA section 110(a)(2)(D) requirements apply to a state
and are not linked with a particular nonattainment area's designation
and classification in that state. The interstate transport SIP
submittal requirements, where applicable, continue to apply to a state
regardless of the designation of any one area in the state. Thus, EPA
has determined that these requirements are not applicable requirements
for purposes of redesignation. Instead, EPA has determined that the
requirements
[[Page 74582]]
linked with a particular nonattainment area's designation and
classifications are the relevant measures, i.e., the requirements that
must be met, for EPA to redesignate an area.
In addition, EPA has determined that the other CAA section
110(a)(2) elements not connected with nonattainment plan submissions
and not linked with an area's attainment status are not applicable
requirements for purposes of redesignation because the area will still
be subject to these requirements after it is redesignated. EPA
concludes that the CAA section 110(a)(2) and part D requirements, which
are linked with a particular area's designation and classification, are
the relevant measures to evaluate in reviewing a redesignation request,
and that section 110(a)(2) elements not linked to the area's
nonattainment status are not applicable for purposes of redesignation.
EPA has applied this interpretation consistently in many
redesignations.\19\
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\19\ See, e.g., 81 FR 4420 (July 17, 2006) (final redesignation
for the Sullivan County, Tennessee area); 79 FR 43655 (July 28,
2014) (final redesignation for Bellefontaine, Ohio lead
nonattainment area); 61 FR 53174-53176 (October 10, 1996) and 62 FR
24826 (May 7 1997) (proposed and final redesignation of Reading,
Pennsylvania ozone nonattainment area); 61 FR 20458 (May 7 1996)
(final redesignation for Cleveland-Akron-Lorain, Ohio ozone
nonattainment area); 60 FR 62748 (December 7, 1995) (final
redesignation of Tampa, Florida ozone nonattainment area); See also
65 FR 37879, 37890, (June 19, 2000) (discussing this issue in final
redesignation of Cincinnati, Ohio 1-hour ozone nonattainment area);
and 66 FR 50399 (October 19, 2001) (final redesignation of
Pittsburg, Pennsylvania 1-hour ozone nonattainment area).
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EPA's review of the Montana SIP shows that the State has satisfied
the general SIP requirements under section 110(a)(2) of the CAA, to the
extent they are applicable for the purposes of redesignation. Moreover,
EPA has previously approved provisions of Montana's SIP as
demonstrating compliance with the CAA section 110(a)(2) requirements
for the 1997 annual PM2.5 NAAQS. See 78 FR 45864 (July 30,
2013). Therefore, EPA proposes to determine that MDEQ has met all
general SIP requirements for the Libby Area that are applicable for
purposes of redesignation under section 110 of the CAA.
2. Part D Requirements
Subparts 1 and 4 of part D, title 1 of the CAA contain air quality
planning requirements for PM2.5 nonattainment areas. Subpart
1 contains general requirements for all nonattainment areas of any
pollutant, including PM2.5, governed by a NAAQS. Subpart 1
requirements include, among other things, provisions for RACM, RFP,
emissions inventories, contingency measures, transportation conformity
and general conformity. Subpart 4 contains specific planning and
scheduling requirements for PM2.5 nonattainment areas.
Sections 189(a), (c), (e) requirements apply specifically to Moderate
PM2.5 nonattainment areas and include an approved permit
program for construction of new and modified major stationary sources,
provisions for RACM, an attainment demonstration, quantitative
milestones demonstrating RFP toward attainment by the applicable
attainment date, and provisions to ensure that the control requirements
applicable to major stationary sources of PM2.5 precursors,
except where the Administrator has determined that such sources do not
contribute significantly to PM2.5 levels that exceed the
NAAQS in the area.
We address the applicability of these requirements to this action
in the following sections.
3. Subpart 1, Section 172 Requirements
Section 172(c) contains general requirements for nonattainment area
plan provisions. A thorough discussion of these requirements may be
found in the General Preamble. See 57 FR 13538 (April 16, 1992). EPA's
longstanding interpretation is that certain planning requirements
designed to get a nonattainment area to attainment of the NAAQS are not
``applicable'' for purposes of CAA section 107(d)(3)(E)(ii) and (v) and
therefore need not be approved into the SIP before EPA can redesignate
the area. In the General Preamble, EPA set forth its interpretation of
applicable requirements for purposes of evaluating redesignation
requests when an area is attaining the standard. See 57 FR 13564. EPA
noted that requirements for RFP and other measures designed to provide
for an area's attainment do not apply in evaluating redesignation
because those nonattainment planning requirements ``have no meaning''
for an area that is attaining the standard. Id. This interpretation is
also set forth in the Calcagni Memorandum.
EPA's understanding of CAA section 172 also forms its basis on its
Clean Data Policy. Under the Clean Data Policy, EPA promulgates a
determination of attainment, published in the Federal Register, which
is subject to notice-and-comment rulemaking, and this determination
formally suspends a state's obligation to submit most of the attainment
planning requirements that would otherwise apply, including an
attainment demonstration and planning SIPs to provide for RFP, RACM,
and contingency measures under CAA section 179(c)(9). The Clean Data
Policy has been codified in regulations regarding the implementation of
the ozone and PM2.5 NAAQS. See e.g., 70 FR 71612 (November
29, 2005) and 72 FR 20586 (April 25, 2007).
Because the Libby Area is attaining the 1997 annual
PM2.5 NAAQS, the attainment planning obligations in CAA
section 172, including the requirement to submit an attainment
demonstration and RACM (172(c)(1)), RFP (172(c)(2)), and contingency
measures (172(c)(9)) are not considered ``applicable'' requirements for
redesignation purposes under CAA section 107(d)(3)(E)(ii) and (v). In
any case, Montana submitted these elements as part of the Moderate SIP
requirements on March 26, 2008, and EPA approved them on March 17,
2011.\20\
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\20\ See 76 FR 14584.
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Section 172(c)(3) of the CAA requires a comprehensive, accurate,
current inventory of actual emissions from all sources of relevant
pollutant(s) in nonattainment areas. EPA's March 17, 2011 approval of
Montana's March 26, 2008 SIP submission included a 2005 base-year
emissions inventory for the Libby Area. Montana also included an
emissions inventory for calendar year 2014 with the June 24, 2020 SIP
submittal of the LMP for the Libby Area. The 2001 Wegman Memorandum
states that an attainment inventory should represent emissions during
the same 5-year period associated with the air quality data used to
determine that the area meets the requirements of the LMP option. In
addition, EPA reviewed an updated 2017 emissions inventory \21\ in its
analysis for the Libby PM2.5 LMP.
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\21\ Available in the docket for this proposed rulemaking.
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Section 172(c)(4) requires the identification and quantification of
allowable emissions for major new and modified stationary sources in an
area, and section 172(c)(5) and 189(a)(1)(A) requires source permits
for the construction and operation of new and modified major stationary
sources anywhere in the nonattainment area. EPA approved the current
Montana NSR program for PM2.5 on July 18, 1995. See 60 FR
36715. Having a fully approved nonattainment NSR program is not an
applicable requirement for this action; nonetheless we have approved
the State's program.\22\
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\22\ A detailed rationale for this view is described in the
memorandum from Mary Nichols, Assistant Administrative for Air and
Radiation, dated October 14, 1994, entitled, ``Part D New Source
Review Requirements for Areas Requesting Redesignation to
Attainment.''
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Section 172(c)(7) requires the SIP meet the applicable provisions
of CAA
[[Page 74583]]
section 110(a)(2). EPA believes Montana's June 24, 2020 SIP submission
pertaining to the Libby Area meets the requirements of section
110(a)(2).
4. Subpart 1, Section 176 Conformity Requirements
Section 176(c) of the CAA requires states to establish the criteria
and procedures to ensure that federally supported or funded projects
conform to the air quality planning goals in the applicable SIP. The
requirement to determine conformity applies to transportation plans,
programs and projects that are developed, funded, or approved under
title 23 of the United States Code (U.S.C.) and the Federal Transit Act
(transportation conformity) as well as to other federally supported or
funded projects (general conformity). State transportation conformity
SIP revisions must be consistent with federal conformity regulations
relating to consultation, enforcement, and enforceability that EPA
promulgated pursuant to its authority under the CAA.
Although EPA interprets the conformity SIP requirements \23\ as not
applying for purposes of evaluating the redesignation request under
section 107(d)(3) \24\ we note that Montana has an approved conformity
SIP. See 66 FR 48561 (September 21, 2001).
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\23\ CAA section 176(c)(4)(E) requires states to submit
revisions to their SIPs to reflect certain federal criteria and
procedures for determining transportation conformity.
\24\ EPA believes that this interpretation is reasonable because
state conformity rules are still required after redesignation and
federal conformity rules apply where states rules have not been
approved. See Wall v. EPA, 265 F.3d 426 (6th Cir., 2001) (upholding
this interpretation); 60 FR 62748 (December 7, 1995).
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5. Subpart 4 Requirements
As discussed in Section I of this document, in NRDC v. EPA, the
D.C. Circuit held that EPA should have implemented the 1997
PM2.5 annual NAAQS pursuant to the particulate matter-
specific provisions of Subpart 4. On remand, EPA identified all areas
designated nonattainment for either the 1997 or the 2006
PM2.5 NAAQS, including the Libby Area, as Moderate
nonattainment for purposes of Subpart 4 in the Classifications and
Deadlines Rule. Moderate nonattainment areas are subject to the
requirements of CAA sections 189(a), (c), and (e), including: (1) an
approved permit program for construction of new and modified major
stationary sources (section 189(a)(1)(A)); (2) an attainment
demonstration, (section 189(a)(1)(B)); (3) provisions for RACM (section
189(a)(1)(C)); (4) quantitative milestones demonstrating RFP toward
attainment by the applicable attainment date (section 189(c)); and (5)
precursor control (section 189(e)).
With respect to the specific attainment planning requirements under
Subpart 4,\25\ EPA applies the same interpretation that it applies to
attainment planning requirements under Subpart 1 or any other
pollutant-specific subparts. That is, under its long-standing
interpretation of the CAA, where an area is already attaining the
standard, EPA does not consider those attainment planning requirements
to be applicable for purposes of evaluating a request for
redesignation, that is, CAA section 107(d)(3)(E)(ii) or (v), because
requirements that are designed to help an area achieve attainment no
longer have meaning where an area is already meeting the standard. EPA
is therefore proposing to determine that the specific attainment
planning requirements under Subpart 4 are not applicable for evaluating
Montana's redesignation request.
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\25\ These planning requirements include the attainment
demonstration, qualitative milestone requirements, and RACM
analysis.
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CAA section 189(e) provides that control requirements for major
stationary sources of direct PM10 (including
PM2.5) shall also apply to particulate matter precursors
from those sources, except where EPA determines that major stationary
sources of such precursors do not contribute significantly to
PM10 levels that exceed the standard in the area. The CAA
does not explicitly address whether it would be appropriate to include
a potential exemption from precursor controls for all source categories
under certain circumstances. In implementing Subpart 4 with regard to
controlling PM10, EPA permitted states to determine that a
precursor was ``insignificant'' where the state could show in its
attainment plan that it would expeditiously attain without adoption of
emission reduction measures aimed at that precursor. This approach was
upheld in the Association of Irritated Residents v. EPA, 423 F.3d 989
(9th Cir. 2005) and extended to PM2.5 implementation in the
PM2.5 SIP Requirements Rule. A state may develop its
attainment plan and adopt RACM that target only those precursors that
are necessary to control for purposes of timely attainment. See 81 FR
58010 at 58020 (August 24, 2016).
For the Libby Area, a precursor exemption analysis under section
189(e) and EPA's implementing regulations is not an applicable
requirement that needs to be fully approved in the context of a
redesignation under CAA section 107(d)(3)(E)(ii) since the Area is
already in attainment which demonstrates that precursors contribution
is insignificant. Therefore, measures aimed at the precursors are not
needed.
As discussed previously in this document, for areas that are
attaining the standard, EPA does not interpret attainment planning
requirements of Subparts 1 and 4 to be applicable requirements for
purposes of redesignating an area to attainment. On July 14, 2015, EPA
approved that the Libby Area had attained the 1997 annual
PM2.5 NAAQS by the Area's statutory attainment date. The
Libby Area has expeditiously attained the 1997 annual PM2.5
NAAQS, and therefore, no additional controls of any pollutant,
including any PM2.5 precursor, are necessary to bring it
into attainment. In section V of this document, we find that the Libby
Area continues to attain the NAAQS. EPA has determined that the Libby
Area has attained the standard due to permanent and enforceable
emissions reductions. Further, as set forth in section IV.C of this
document, we believe that the Libby PM2.5 LMP demonstrates
continued maintenance of the 1997 annual PM2.5 NAAQS
standard through 2031 which also demonstrates that the PM2.5
precursors are insignificant. Taken together, these factors support our
conclusion that PM2.5 precursors are adequately
controllable.
B. Has the state demonstrated that air quality improvement is due to
permanent and enforceable reductions?
In order to approve a redesignation from nonattainment to
attainment, section 107(d)(3)(E)(iii) of the CAA requires EPA to
determine that the improvement in air quality is due to emission
reductions that are permanent and enforceable, and that the improvement
results from the implementation of the applicable SIP and applicable
federal air pollution control regulations and other permanent and
enforceable regulations. Under this criterion, a state must be able to
reasonably attribute the improvement in air quality to emissions
reductions that are permanent and enforceable. Attainment resulting
from temporary reductions in emission rates (e.g., reduced production
or shutdown due to temporary adverse economic conditions) or unusually
favorable meteorology would not qualify as an air quality improvement
due to permanent and enforceable emission reductions. See Calcagni
Memorandum at 4. In its demonstration that improvements in air quality
are reasonably attributable to emissions reductions that are permanent
[[Page 74584]]
and enforceable, Montana evaluated several factors: \26\ the
composition of PM2.5 in the nonattainment area; control
measures that have been implemented since the area was redesignated to
nonattainment; changes to the emissions inventory over time; and
meteorological and economic trends. In its evaluation, Montana
identified two fugitive area sources contributing to PM2.5
concentrations in the nonattainment area: wood combustion and tailpipe
emissions. Eighty-two percent of the PM2.5 concentrations
during the baseline study year of 2005 was attributed to wood
combustion. Wood combustion impacts represented both residential and
small commercial space heating, and outdoor burns. The State identified
emission reductions from only the wood combustion category in the
attainment plan; the plan did not take credit for reductions from
mobile source tailpipe emissions due to federal tailpipe standards or
fleet turnover.
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\26\ See Montana's attainment plan for the Libby Area, approved
on March 17, 2011 (76 FR 14584).
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In its approved Moderate nonattainment plan, Montana adopted
permanent and enforceable rules from the Lincoln County Air Pollution
Control Program. This program includes rules that reduce
PM2.5 impacts in the nonattainment area resulting in
attainment of PM2.5 NAAQS.\27\ The air pollution control
rules in Chapter 1, Subchapters 1 through 4 of the Lincoln County Air
Pollution Control Program, address solid fuel burning devices, re-
entrained road dust control, and outdoor burning regulations. These
rules are part of the Lincoln County Health Department's Health and
Environmental Rules in Chapter 1. The rules contain the following
subchapters, all designed to help Lincoln County attain the
PM2.5 NAAQS:
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\27\ See Section 1.3 in the Libby Area SIP submission. Available
in the docket for this proposed rulemaking.
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Subchapter 1--(75.1.100-106)--General Provisions;
Subchapter 2--(75.1.200-206,208)--Solid Fuel Burning
Device Regulations;
Subchapter 3--(75.1.301-308)--Dust Control Regulations;
and
Subchapter 4--(75.1.401-408)--Outdoor Burning Regulations.
The regulations in Lincoln County's Subchapter 2 require that solid
fuel burning devices be permitted by the Lincoln County Environmental
Health Department. The regulations restrict the material allowed for
combustion and prohibit visible emissions greater than 20 percent
opacity. Lincoln County will call Air Pollution Alerts \28\ when
particulate matter concentrations are more than 80 percent of the 24-
hour standard and at that time, solid fuel burning devices are not
allowed to operate unless the device has received an exemption. A
provision allows exempt devices to be operated during an alert, but
only with an opacity of 10 percent or less.
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\28\ See 75.1.206, Lincoln County Air Pollution Control Program.
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Although re-entrained road dust is not an identified emission
source category, Subchapter 3 of the Lincoln County rules address re-
entrained dust from roads, parking lots and commercial lots by
requiring dust abatement and control. These road dust regulations apply
within the regulated road sanding and sweeping district as defined in
the regulation. Vehicular operations within the district are only
allowed on paved surfaces within the district. To control ice on the
roads, liquid de-icing agents and de-icing salts should be used.
Sanding material is not allowed unless the Lincoln County Environmental
Health Department declares an emergency and then only sanding material
that meets specific durability, abrasion, and fine concentrations are
allowed. Roads are to be maintained using a schedule of prioritized
street sweeping and flushing to remove carry-on or applied materials.
Commercial operations shall also implement measures to prevent
depositing material on yards/lots, suppress dust, and clean adjoining
roadways.
Lincoln County's Subchapter 4 addresses outdoor burning and
restricts non-essential outdoor burning, promoting alternative disposal
methods and recycling, and setting standards to minimize emissions when
outdoor burning is necessary. These rules apply to both the air
pollution control district which is the same area as the Libby
nonattainment area, and the Impact Zone L, which extends beyond the
nonattainment area. The rules specify which materials and activities
are prohibited for outdoor burning. Residential outdoor burning is only
allowed in the month of April while management burns are allowed from
April through October. Burning outside these months requires additional
approval from the Lincoln County Health Department. Burners must obtain
a burn permit from the Department and may only conduct their burn if
meteorological conditions have good air dispersion characteristics, as
determined by the Department.
Montana has determined that most of the emissions reductions from
the wood combustion source category are attributed to the Lincoln
County residential wood combustion rules. These rules control
residential and small commercial wood combustion used for space heating
through a wood stove permit program. The rules restrict the
installation and operation of wood stoves to times with good air
quality dispersion. Lincoln County also has outdoor open burning rules
that require burns to be permitted and approved to ensure the burns
occur during favorable meteorological conditions.
Montana evaluated emissions from residential wood burning
contributing to PM2.5 in Libby, Montana. Table 2.3 in the
June 24, 2020 Libby Area SIP submission displays the 2005 actual annual
emissions, which are considered the annual baseline emissions for
Libby. Additionally, the table shows the annual emissions from the 2014
National Emissions Inventory (NEI). As shown in the Table 2.3,
emissions for residential wood burning in 2014 have decreased more than
85 percent compared to the baseline emissions in 2005. The total
emissions for area source categories for 2014 total emissions have
decreased more than 62 percent compared to the 2005 baseline emissions.
In addition, Montana has adopted permitting requirements for major
stationary sources or major modifications located in the nonattainment
areas including Libby, Montana. They are located in the Administrative
Rules of Montana (ARM) 17.8.901 through 17.8.906. These rules require
all new sources or modifications to use the lowest achievable emission
rate (LAER). Sources must obtain emission reduction offsets in tons per
year (tpy) which provide a positive net air quality benefit in the
nonattainment area using a one to one offset and must be from the same
source or another emissions source within the same nonattainment area.
There must be demonstrated improvement to the PM2.5
nonattainment with permanent, quantifiable, and federally enforceable
reductions. A reduction of actual emissions, not potential emissions,
must occur before a new source can be permitted to operate.
In addition, Montana has a federally enforceable permitting program
for minor sources in ARM, Title 17 Chapter 8, Subpart 7 that addresses
PM2.5 emissions. These rules require sources that emit 25
tpy or more of PM2.5 to ensure the nonattainment area is not
negatively affected. Beginning in May 2019, Montana began requiring
registration of all sized asphalt plants, concrete plants, mineral
crushers, and
[[Page 74585]]
mineral screens. The registration program establishes conservative
operational restrictions on these portable sources to prevent
degradation of the air quality in nonattainment areas and elsewhere.
Not only has air quality in the Libby Area benefited from the local
district and State rules discussed previously, but the Area has also
benefitted from emission reductions from federal measures including
federal tailpipe standards and the Federal Motor Vehicle Control
Program. Federal tailpipe standards were designed to reduce vehicle
emissions, including PM2.5. The previous control plan did
not take credit for the PM2.5 reductions resulting from
lower federal vehicle emissions standards and vehicle fleet turnover in
the nonattainment area. The federal tailpipe standards and vehicle
turnover will continue to reduce future impacts and meet the
requirements of the 1990 CAA Amendments. The Federal Motor Vehicle
Control Program controls tailpipe emissions and evaporative emission
standards for new vehicles. Tailpipe impacts were less than one percent
of the Libby Area during the 2005 baseline year.\29\ The
PM2.5 impact reductions are supported by lower fleet vehicle
fleet emissions as fleet turnover continues.
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\29\ See Table 2.3 in the Libby Area SIP submission. Available
in the docket for this proposed rulemaking.
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Based upon the previously listed actions by Montana in the
submitted maintenance plan, EPA finds that the improvement in air
quality in the Libby Area is the result of permanent and enforceable
emissions reductions from a combination of EPA-approved local and State
control measures and federal control measures. As such, we believe the
criterion for redesignation set forth in CAA section 107(d)(3)(E)(iii)
is satisfied.
C. Does the Area have a fully approved maintenance plan pursuant to
section 175A of the CAA?
For redesignating a nonattainment area to attainment, the CAA
requires EPA to determine that the area has a fully approved
maintenance plan pursuant to section 175A of the CAA (CAA section
107(d)(3)(E)(iv)). In conjunction with its request to redesignate the
Libby Area to attainment for the 1997 annual PM2.5 NAAQS,
Montana submitted a SIP revision to provide for the maintenance of the
1997 annual PM2.5 NAAQS for at least 10 years after the
effective date of redesignation to attainment. EPA believes that this
maintenance plan meets the requirements for approval under section 175A
of the CAA for the reasons discussed in this section.
Section 175A of the CAA sets forth the elements of a maintenance
plan for areas seeking redesignation from nonattainment to attainment.
Under section 175A, the plan must demonstrate continued attainment of
the applicable NAAQS for at least 10 years after the Administrator
approves a redesignation to attainment. Because the 1997 primary annual
PM2.5 NAAQS will be revoked for the Libby Area if it is
redesignated to attainment, Montana is not required to submit a second
10-year maintenance plan for the 1997 primary annual PM2.5
NAAQS. See 81 FR 58010, 58144. To address the possibility of future
NAAQS violations, the maintenance plan must contain such contingency
measures, as EPA deems necessary, to assure prompt correction of any
future 1997 annual PM2.5 NAAQS violations. The Calcagni
Memorandum provides further guidance on the content of a maintenance
plan, explaining that a maintenance plan should address five
requirements: the attainment emissions inventory; maintenance
demonstration; monitoring; verification of continued attainment; and a
contingency plan. As is discussed here, EPA finds that Montana's
maintenance plan includes all the necessary components and is thus
proposing to approve it as a revision to the Montana SIP.
1. Attainment Emissions Inventory
As discussed previously, EPA is proposing to determine that the
Libby Area is attaining the 1997 annual PM2.5 NAAQS based on
a monitoring data for the time period from 2014-2021. Montana selected
2014 as the attainment emission inventory year. The attainment
inventory identifies the level of emissions in the Area that is
sufficient to attain the 1997 annual PM2.5 NAAQS. Montana
began development of the attainment inventory by first generating a
baseline emissions inventory for the Libby Area. Montana selected 2005
as the base year for developing a comprehensive emissions inventory for
direct PM2.5 and the PM2.5 precursors
SO2, NOX, VOCs, and ammonia. See 76 FR 14584
(March 17, 2011). The Wegman Memorandum states that an attainment
inventory should represent emissions during the same 5-year period
associated with the air quality data used to determine that the area
meets the applicability requirements of the LMP option. The Libby LMP,
provided in Montana's June 24, 2020 SIP submission, includes an
emission inventory from 2014, representative of the 2014-2021 time
period which served as the 5-year period relied upon in limited
maintenance plans as meeting the air quality data requirements of the
Wegman Memorandum.\30\
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\30\ The emissions inventory included in the Libby Area SIP
submission is the 2014 NEI. The NEI is a composite of data from many
different sources, with PM data coming primarily from EPA models as
well as from state, tribal, and local air quality management
agencies. Different data sources use different data collection
methods, and many of the emissions data are based on estimates
rather than actual measurements. EPA considers the 2014 NEI
representative of the period from 2014-2021 because Montana provided
comparable vehicle miles traveled (VMT) data in their submission.
See Libby Area SIP submission, Appendix A, Montana Department of
Transportation Future VMT Projections, p. A-1 in docket for this
proposed rulemaking.
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2. Maintenance Demonstration
Montana's SIP submission for the Libby Area employs the CDV method
laid out in the 2001 Wegman Memorandum to demonstrate that the Area is
eligible for an LMP. As noted previously, the CDV calculation from the
Wegman Memorandum represents the highest design value an area could
have before it would violate the NAAQS given a 1 in 10 probability--
that is, if the area's current ADV (based on the most recent five years
of data) is less than the CDV, there is a less than 1 in 10
probabilities that the area will violate in the future. The State's
submission calculates the ADV as 10.9 [micro]g/m\3\ and calculates the
site-specific CDV as 14.1 [micro]g/m\3\ using the Libby Area monitor
data from 2014-2018. Therefore, the State's submission showed the Libby
ADV is less than the CDV, but because of the time that has elapsed
since the State's submission, EPA has also analyzed more recent data
that are available in AQS and have been certified by the MDEQ.
To calculate the ADV we averaged the most recent five design values
for the PM2.5 annual standard. Since each design value is
calculated by averaging three years of valid annual means, the average
of the last five design values includes data from the most recent 7-
year period (2014-2021). Table 3 presents the most recent annual
PM2.5 NAAQS design values for 2017-2021 and presents the
resulting ADV of 13.2 [micro]g/m\3\.
To calculate the CDV we use the most recent five years of design
values and their variability with the equation presented in the Wegman
Memorandum (Table 3). The resulting site-specific CDV is calculated to
be 14.6 [micro]g/m\3\ (Table 5). Therefore, the ADV (13.2 [micro]g/
m\3\) falls below the site-specific CDV of
[[Page 74586]]
14.6 [micro]g/m\3\ and thus meets the first criterion for LMP
eligibility.\31\
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\31\ See Libby PM2.5 CDV Calculations in docket for
this proposed rulemaking.
Table 3--Annual PM2.5 NAAQS Design Values ([micro]g/m\3\) \32\
--------------------------------------------------------------------------------------------------------------------------------------------------------
Average of most recent
2017 Design value (2015- 2018 Design value (2016- 2019 Design value (2017- 2020 Design value (2018- 2021 Design value 3-year design values
2017) * 2018) * 2019) * 2020) * (2019-2021) * (ADV)
--------------------------------------------------------------------------------------------------------------------------------------------------------
13.0 12.9 13.4 13.3 13.3 13.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table 4--Eligibility Calculation Equations
------------------------------------------------------------------------
------------------------------------------------------------------------
Critical Design Value.................. CDV = NAAQS/(1 + (tc x CV))
Coefficient of Variation............... CV = [sigma]/ADV
Projected DV due to Motor Vehicle Projected DV = ADV + (VMTpi x
Growth over 10 years. DVmv)]
------------------------------------------------------------------------
ADV = Average of 3-year design values.
DV = Design value.
DVmv = motor vehicle design value based on on-road mobile portion of the
attainment year inventory.
NAAQS = Applicable standard (15 [mu]g/m\3\).
[sigma] = standard deviation of design values.
tc = Critical t-value (based on the one-tail student's t-distribution,
at a significance level of 0.10).
VMTpi = Projected percent increase in vehicle miles traveled (VMT) over
the next 10 years.
Table 5--Calculation of the CDV Using 2017-2021 Design Values
------------------------------------------------------------------------
------------------------------------------------------------------------
NAAQS.................................. 15.0 [mu]g/m\3\
Tc..................................... 1.533
ADV (2017-2021)........................ 13.2 [mu]g/m\3\
[Sigma]................................ 0.2168 [mu]g/m\3\
CV..................................... 0.0164
CDV = [NAAQS/(1 + tc x CV)]............ 14.6 [mu]g/m\3\
------------------------------------------------------------------------
In addition to having an ADV that is at or below the site-specific
CDV, the 2001 Wegman Memorandum also provides a methodology for
calculating a margin of safety factor based on expected growth in
mobile source emissions. The memo lays out in Attachment B a motor
vehicle regional emissions analysis test, which is designed to account
for an area's expected change in vehicle miles traveled, to determine
whether increased emissions from on-road mobile sources could, in the
next 10 years, increase concentrations in the area and threaten the
assumption of maintenance that underlies LMP policy. In its June 24,
2020 SIP submission, Montana employed the motor vehicle regional
emissions analysis test outlined in Attachment B of the Wegman
Memorandum to demonstrate that the Libby Area's expected growth in
mobile source emissions would not threaten maintenance of the NAAQS.
Using data from 2014-2018 the State calculated that due to growth in
mobile source emissions the ADV may increase from 10.9 [micro]g/m\3\ to
11.1 [micro]g/m\3\ in the next 10 years, but that 11.1 [micro]g/m\3\ is
still below the margin of safety as defined by the site-specific CDV
(14.1 [micro]g/m\3\). EPA has also examined more recent data to confirm
that even with updated information, the test continues to show that
anticipated growth in mobile source emissions should not interfere with
the Libby Area's maintenance of the 1997 annual PM2.5 NAAQS.
Using design values from 2017-2021, we calculated that due to expected
growth in mobile source emissions, the ADV may increase from 13.2
[micro]g/m\3\ to 13.5 [micro]g/m\3\ in the next 10 years, but that 13.5
[micro]g/m\3\ is still below the margin of safety as defined by the
site-specific CDV (14.6 [micro]g/m\3\). For the calculations used to
determine how the Libby Area passed the motor vehicle regional analysis
test, see Table 6.\33\
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\32\ In Table 3, (years)* is referring to what data was included
in the calculation for each 3-year design value.
\33\ See Memo to File, Libby MT Motor Vehicle Regional Emission
Analysis in docket for this proposed rulemaking.
Table 6--Motor Vehicle Regional Emissions Analysis Test Calculations
------------------------------------------------------------------------
------------------------------------------------------------------------
ADV (2017-2021)........................ 13.2 [micro]g/m\3\
VMTpi.................................. 11.56%
DVmv................................... 2.5 [micro]g/m\3\
Calculated [ADV + (VMTpi x DVmv)]...... 13.5 [micro]g/m\3\
------------------------------------------------------------------------
The 2001 Wegman Memorandum also indicates that once a state has an
approved LMP, the state will be expected to determine, on an annual
basis, that the LMP criteria are still being met. If the state
determines that the LMP criteria are not being met, it should take
action to reduce PM2.5 concentrations enough to requalify
for the LMP. One possible approach a state could take is to implement
contingency measures. For a description of contingency provisions
included in the Libby LMP, see section 3.6 of Montana's June 24, 2020
SIP submission.
Although the State flagged some PM2.5 values as
potentially affected by exceptional events, such as wildfire
[[Page 74587]]
smoke, this action utilizes all quality-assured monitoring data from
Libby. A 2019 memo from Richard Wayland and Anna Wood regarding
additional methods, determinations, and analyses to modify air quality
data beyond exceptional events,\34\ indicates that monitoring data
could qualify for exclusion for use in calculating air quality design
values in support of a NAAQS LMP submission and any subsequent yearly
design value calculations for areas with approved LMPs. The memorandum
states that such data exclusion requests will be treated in a manner
analogous to the treatment of exceedance data under the Exceptional
Events Rule (EER). Since the Libby Area qualifies for the LMP option
without the removal of any demonstrated values, the flagged data have
no regulatory significance and therefore the demonstrated values are
included in the calculations and remain in AQS. Additional information
on the EER can be found in 40 CFR 50.14 and 40 CFR 51.930.
---------------------------------------------------------------------------
\34\ See the memorandum from Richard Wayland, Director of Air
Quality Assessment Division and Anna Marie Wood, Director of Air
Quality Policy Division, dated April 4, 2019, entitled, ``Additional
Methods, Determinations, and Analyses to Modify Air Quality Data
Beyond Exceptional Events.''
---------------------------------------------------------------------------
Pursuant to the Wegman Memorandum, the State's approved maintenance
plan should include an emissions inventory (attainment inventory) which
can be used to demonstrate attainment of the NAAQS. The inventory
should represent emissions during the same 5-year period associated
with air quality data used to determine whether the area meets the
applicability requirements of the LMP option. The state should review
its inventory every three years to ensure emissions growth is
incorporated in the attainment inventory, if necessary. In this
instance, Montana completed an attainment year inventory for 2014 for
the Libby Area. EPA has reviewed the 2014 emissions inventories and
determined that they are appropriate for this plan.
3. Monitoring Network
The PM2.5 monitoring network for the Libby Area has been
developed and maintained in accordance with federal siting and design
criteria in 40 CFR part 58, appendices D and E and in consultation with
EPA Region 8. In section 3.5 of the Libby LMP, located within Montana's
June 24, 2020 SIP submission, Montana states that it will continue to
operate its monitoring network to meet EPA requirements at 40 CFR part
58 and identify any issues or adjustments via the annual Ambient Air
Monitoring Network Plan or formal communication. EPA approved Montana's
2021 monitoring plan on November 16, 2021.\35\
---------------------------------------------------------------------------
\35\ See MT AMNP Approval Letter 2021 in docket for the proposed
rulemaking.
---------------------------------------------------------------------------
4. Verification of Continued Attainment
Montana, through MDEQ, has the legal authority to enforce and
implement the requirements of the Libby LMP. This includes the
authority to adopt, implement, and enforce any subsequent emissions
control contingency measures determined to be necessary to correct
future PM2.5 attainment problems.
In demonstrating maintenance, continued attainment of the NAAQS can
be verified through operation of an appropriate air quality monitoring
network. The Calcagni Memorandum (p.11) states that the maintenance
plan should contain provisions for continued operation of air quality
monitors that will provide such verification. As discussed in section V
of this document, PM2.5 is currently monitored by MDEQ
within the Libby Area. In section 3.5 of Montana's submitted
maintenance plan, MDEQ intends to maintain an appropriate
PM2.5 monitoring network and review monitoring and emissions
data through the maintenance period.
MDEQ will track the progress of the maintenance plan by performing
future reviews of triennial emission inventories for the Libby Area as
required in the Air Emissions Reporting Rule (AERR). Emissions
information will be compared to the attainment year to assure continued
compliance with the annual PM2.5 standard.
5. Contingency Provisions
Section 175A(d) of the CAA requires that the maintenance plan
contains contingency provisions to assure that the state will promptly
correct any violation of the relevant PM2.5 NAAQS that may
occur after the redesignation of the area to attainment. Such
provisions must include a requirement that the state will implement all
measures with respect to the control of the air pollutant concerned
that were contained in the SIP for the area before redesignation of the
area as an attainment area. EPA's redesignation guidance notes that the
state is not required to have fully adopted contingency measures that
will take effect without further action by the state. As such, the
contingency plan should ensure that the state has the capacity to adopt
the contingency measures expediently if the need were triggered.
Therefore, the primary elements of this contingency plan involve the
tracking and triggering mechanisms to determine when contingency
measures would be necessary and a process for implementing appropriate
control measures.
Montana will continue to monitor and analyze PM2.5
concentrations to determine continued maintenance of the relevant
PM2.5 NAAQS. In accordance with 40 CFR part 58, MDEQ will
continue to operate the Libby monitor (Site ID 30-053-0018).
If the State determines the Libby Area has exceeded the 1997 annual
PM2.5 NAAQS, the triggering of the contingency plan does not
automatically require a revision of the SIP, nor is the Area
necessarily redesignated once again to nonattainment. Instead, MDEQ
will have an appropriate timeframe to correct the violation with
implementation of one or more adopted contingency measures. If
violations continue to occur, additional contingency measures may need
to be adopted until the violations are corrected.
Montana has adopted a contingency provision to address future
PM2.5 air quality problems. The contingency provisions in
the Libby PM2.5 LMP are contained in section 3.6. of
Montana's June 24, 2020, SIP submission. MDEQ identifies the following
steps if a violation occurs, and the State triggers the contingency
plan:
1. Within 12 months of an exceedance notification, MDEQ and the
local government in the Libby Area will commence an analysis to review
information about historical exceedances of the standard, the
meteorological conditions related to recent exceedance(s), most recent
growth, and emissions, and if the possibility of an exceptional event
occurred. MDEQ will develop appropriate contingency measure(s) to
correct the violation of the PM2.5 standard.
2. Under the 2016 revisions to the Treatment of Data Influenced by
Exceptional Events Rule (81 FR 68216), MDEQ will confer with EPA Region
8 regarding whether any flagged exceptional events would meet the
criteria of a regulatory decision, and if so, a determination would be
made on whether to move forward with producing a demonstration and if
that would trigger contingency measures.
3. If MDEQ and the local government in the Libby Area finds locally
adopted control measures to be inadequate, MDEQ and the local
government will adopt state-enforceable measures as deemed necessary by
MDEQ to prevent additional exceedances or violations.
[[Page 74588]]
Measures to be considered include implementation of Libby's Contingency
Rules 75.1.208 and 75.1.307, as spelled out in Montana's Libby
PM2.5 attainment plan, the use of deciphers, additional
street cleaning, etc.
Upon our review, we find that the contingency provisions of the
Libby PM2.5 LMP satisfy the pertinent requirements of
section 175A of the CAA.
D. Transportation and General Conformity
The requirements for transportation and general conformity are
found in CAA section 176(c). Conformity to the SIP means that
transportation-related actions (transportation conformity) and other
federal actions (general conformity) will not cause or contribute to
any new violation of any standard in any area, increase the frequency
or severity of any existing violation of any standard in any area or
delay timely attainment of any standard or any required interim
emission reductions or other milestones in any area (CAA section
176(c)(1)(B)).
As discussed in section II.B, if the proposal is finalized, the
1997 primary annual PM2.5 NAAQS will be revoked in the Libby
Area on the effective date of the redesignation. Beginning on that
date, the Area will no longer be subject to transportation conformity
or general conformity requirements for the 1997 annual PM2.5
NAAQS due to the revocation of the 1997 primary annual PM2.5
NAAQS. See 81 FR 58125-6.
V. What are the effects of EPA's proposed actions?
EPA's proposed actions establish the basis upon which EPA may take
final action on the issues being proposed for approval. Approval of
Montana's redesignation request would change the legal designation of
Lincoln County for the 1997 annual PM2.5 NAAQS, found at 40
CFR part 81, from nonattainment to attainment. The limited maintenance
plan includes contingency measures to remedy any future violations of
the 1997 annual PM2.5 NAAQS and procedures for evaluation of
potential violations.
VI. Proposed Actions
EPA is proposing to: (1) determine that the Libby Area is attaining
the 1997 annual PM2.5 NAAQS based on 2014-2021 data; (2)
approve Montana's plan for maintaining the 1997 annual PM2.5
NAAQS (limited maintenance plan); and (3) redesignate the Libby Area to
attainment for the 1997 annual PM2.5 NAAQS. If finalized,
approval of the redesignation request would change the official
designation of Lincoln County for the 1997 annual PM2.5
NAAQS, found at 40 CFR part 81 from nonattainment to attainment, as
found at 40 CFR part 81.
VII. Statutory and Executive Order Reviews
Under the CAA, redesignation of an area to attainment and the
accompanying approval of a maintenance plan are actions that affect the
status of a geographical area and do not impose any additional
regulatory requirements on sources beyond those imposed by state law. A
redesignation to attainment does not in and of itself create any new
requirements, but rather results in the applicability of requirements
contained in the CAA for areas that have been redesignated to
attainment. Moreover, the Administrator is required to approve a SIP
submission that complies with the provisions of the Act and applicable
federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely proposes to approve state law as meeting federal
requirements and does not impose additional requirements beyond those
imposed by state law. For these reasons, this proposed action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Public Law 104-4);
Does not have Federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Executive Order 12898 (59 FR 7629, February 16, 1994,
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 program,
policies, and activities on minority populations (people of color/
Indigenous people) and low-income populations.
In addition, the SIP is not approved to apply on any Indian
reservation land or in any other area where EPA or an Indian tribe has
demonstrated that a tribe has jurisdiction. In those areas of Indian
country, the proposed rule does not have tribal implications and will
not impose substantial direct costs on tribal governments or preempt
tribal law as specified by Executive Order 13175 (65 FR 67249, November
9, 2000).
List of Subjects
40 CFR Part 52
Environmental protection, Air pollution control, Carbon monoxide,
Greenhouse gases, Incorporation by reference, Intergovernmental
relations, Lead, Nitrogen dioxide, Ozone, Particulate matter, Reporting
and recordkeeping requirements, Sulfur oxides, Volatile organic
compounds.
40 CFR Part 81
Environmental protection, Air pollution control, National parks,
and Wilderness areas.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 1, 2022.
KC Becker,
Regional Administrator, Region 8.
[FR Doc. 2022-26504 Filed 12-5-22; 8:45 am]
BILLING CODE 6560-50-P