Air Plan Approval; ID, Pinehurst PM10, 45830-45835 [2018-19600]
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Federal Register / Vol. 83, No. 176 / Tuesday, September 11, 2018 / Rules and Regulations
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3. Section 52.1770(e), is amended by
adding entries for ‘‘110(a)(1) and (2)
Infrastructure Requirements for 1997
Fine Particulate Matter NAAQS’’,
‘‘110(a)(1) and (2) Infrastructure
Requirements for 2006 Fine Particulate
Matter NAAQS’’, ‘‘110(a)(1) and (2)
Infrastructure Requirements for the 2008
Lead NAAQS’’, ‘‘110(a)(1) and (2)
Infrastructure Requirements for the 2008
8-Hour Ozone NAAQS’’, ‘‘110(a)(1) and
(2) Infrastructure Requirements for the
2010 1-hour NO2 NAAQS’’, ‘‘110(a)(1)
and (2) Infrastructure Requirements for
the 2010 1-hour SO2 NAAQS’’, and
■
‘‘110(a)(1) and (2) Infrastructure
Requirements for the 2012 Annual PM2.5
NAAQS’’ at the end of the table to read
as follows:
§ 52.1770
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Identification of plan.
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(e) * * *
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EPA-APPROVED NORTH CAROLINA NON-REGULATORY PROVISIONS
State effective
date
EPA approval
date
Federal Register citation
Explanation
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4/1/2008
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9/11/2018
9/21/2009
9/11/2018
6/15/2012
9/11/2018
110(a)(1) and (2) Infrastructure Requirements for the 2008 8-Hour Ozone
NAAQS.
110(a)(1) and (2) Infrastructure Requirements for the 2010 1-hour NO2 NAAQS.
11/2/2012
9/11/2018
8/23/2013
9/11/2018
110(a)(1) and (2) Infrastructure Requirements for the 2010 1-hour SO2 NAAQS.
3/18/2014
9/11/2018
110(a)(1) and (2) Infrastructure Requirements for the 2012 Annual PM2.5
NAAQS.
12/4/2015
9/11/2018
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[Insert citation of
publication in Federal Register].
[Insert citation of
publication in Federal Register].
[Insert citation of
publication in Federal Register].
[Insert citation of
publication in Federal Register].
[Insert citation of
publication in Federal Register].
[Insert citation of
publication in Federal Register].
[Insert citation of
publication in Federal Register].
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Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Approved the PSD elements of sections
110(a)(2)(C), 110(a)(2)(D)(i)(II) (prong
3) and 110(a)(2)(J).
Provision
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110(a)(1) and (2) Infrastructure Requirements for 1997 Fine Particulate Matter
NAAQS.
110(a)(1) and (2) Infrastructure Requirements for 2006 Fine Particulate Matter
NAAQS.
110(a)(1) and (2) Infrastructure Requirements for the 2008 Lead NAAQS.
[FR Doc. 2018–19603 Filed 9–10–18; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 81
[EPA–R10–OAR–2017–0582; FRL–9983–
53—Region 10]
Air Plan Approval; ID, Pinehurst PM10
Redesignation, Limited Maintenance
Plan; West Silver Valley 2012 Annual
PM2.5 Emission Inventory
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The EPA is approving the
redesignation request and limited
maintenance plan for the PM10 National
Ambient Air Quality Standard
developed for the City of Pinehurst
PM10 Nonattainment Area and the
Pinehurst PM10 Expansion
Nonattainment Area. This redesignation
will change the status of both areas from
nonattainment to attainment. The
limited maintenance plan for these
contiguous nonattainment areas
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SUMMARY:
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addresses maintenance of the PM10
standard for a ten-year period beyond
redesignation. Related to this action, the
EPA is taking final agency action on the
September 15, 2013, high wind
exceptional event at the Pinehurst
monitoring station. Additionally, the
EPA is finalizing approval of the
emissions inventory for the West Silver
Valley 2012 annual PM2.5
nonattainment area.
section for
additional availability information.
FOR FURTHER INFORMATION CONTACT:
Justin Spenillo at (206) 553–6125, or
spenillo.justin@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, it is
intended to refer to the EPA.
This action is effective on
October 11, 2018.
I. Background Information
II. Response to Comments
III. Final Action
IV. Statutory and Executive Orders Review
DATES:
The EPA has established a
docket for this action under Docket ID
No. EPA–R10–OAR–2017–0582. All
documents in the docket are listed on
the https://www.regulations.gov
website. Although listed in the index,
some information is not publicly
available, e.g., Confidential Business
Information or other information the
disclosure of which is restricted by
statute. Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available through https://
www.regulations.gov, or please contact
the person identified in the FOR FURTHER
ADDRESSES:
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INFORMATION CONTACT
Table of Contents
I. Background Information
On May 11, 2018, the EPA proposed
to approve the redesignation request
and limited maintenance plan (LMP)
submitted by the Idaho Department of
Environmental Quality (IDEQ) on
September 29, 2017, for the City of
Pinehurst PM10 Nonattainment Area and
the Pinehurst PM10 Expansion
Nonattainment Area, collectively
referred to as the Pinehurst PM10
Nonattainment Area (Pinehurst PM10
NAA).
Related to this action, the EPA is
taking final agency action on the EPA’s
concurrence with the IDEQ’s request for
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exclusion of data measured on
September 15, 2013, as a high wind
exceptional event at the Pinehurst
monitoring station, as set forth in the
March 2, 2017 letter to the IDEQ,
included in the docket. The Clean Air
Act (CAA) allows for the exclusion of
air quality monitoring data from design
value calculations when there are
exceedances caused by events, such as
wildfires or high wind events, that meet
the criteria for an exceptional event
identified in the EPA’s implementing
regulations, the Exceptional Events Rule
at 40 CFR 50.1, 50.14 and 51.930. In
2013, emissions from a high wind event
entrained dust and impacted PM10
concentrations recorded at the Pinehurst
monitor. The EPA evaluated the IDEQ’s
exceptional event demonstration for the
flagged values of the 24-hour PM10
NAAQS for September 15, 2013, at the
monitor in Pinehurst, Idaho, with
respect to the requirements of the EPA’s
Exceptional Events Rule and
determined that IDEQ met the rule
requirements.
Separately, the EPA also proposed
approval of the base year emissions
inventory for the West Silver Valley
(WSV) PM2.5 Nonattainment Area
(NAA). Section 172(c)(3) of the CAA
requires a state with an area designated
as nonattainment to submit a
‘‘comprehensive, accurate, current
inventory of actual emissions from all
sources of the relevant pollutant’’ for the
NAA. The IDEQ developed a 2013 base
year emissions inventory for the WSV
annual PM2.5 NAA. The base year
emissions inventory includes data from
2013 and 2014 and in large part was
extracted from the 2014 periodic
emissions inventory which is used to
populate the EPA’s National Emissions
Inventory. The 2013 base year inventory
is one of the three years used to
designate the area as nonattainment.
This base year inventory presents direct
PM2.5 emissions (condensable and
filterable) and emissions of all PM2.5
precursors (NOX, VOCs, NH3, and SO2)
to meet the emissions inventory
requirements of CAA section 172(c)(3)
and 40 CFR 51.1008(a)(1). The EPA has
reviewed the results, procedures, and
methodologies for the WSV Annual
PM2.5 NAA base year emissions
inventory. The EPA determined that the
2013 base year emissions inventory for
the WSV annual PM2.5 NAA met the
requirements of CAA section 172(c)(3)
and 40 CFR 51.1008(a)(1).
An explanation of the CAA
requirements, a detailed analysis of the
submittal, and the EPA’s reasons for
proposing approval were provided in
the notice of proposed rulemaking (83
FR 21976), and will not be restated here.
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The public comment period for this
proposed rule ended on June 11, 2018.
The EPA received adverse comments on
the proposal.
II. Response to Comments
The Idaho Conservation League (ICL)
submitted adverse comments on our
proposed approval of the Pinehurst
PM10 NAA redesignation request and
LMP. Within this section, we have
summarized the adverse comments and
provided our responses. A full copy of
comments received is available in the
docket for this final action.
Comment—Permanent and Enforceable
Emissions Reductions
Summary—The ICL comment letter
asserts the ‘‘EPA must reject Idaho
DEQ’s request for redesignation of the
Pinehurst NAA’’ because the state has
not met the redesignation requirements
in CAA section 107(d)(3)(E)(iii). The ICL
cites the EPA’s September 4, 1992,
guidance, which, among other things,
addresses emissions reductions based
on permanent and enforceable measures
(Memorandum from John Calcagni,
Director, Air Quality Management
Division, EPA Office of Air Quality
Planning and Standards, entitled
‘‘Procedures for Processing Requests to
Redesignate Areas to Attainment’’
(Calcagni Memo)). The ICL comment
letter provides examples of
nonattainment areas redesignated for
PM10 and ozone in Ohio, Colorado, and
Idaho, which use local rules, laws, and
ordinances to provide for permanent
and enforceable emissions reductions.
The comment letter states that the IDEQ
and City of Pinehurst were aware of the
need for permanent and enforceable
measures, citing discussion notes taken
during a 2016 advisory committee
session for the West Silver Valley PM2.5
NAA, an overlapping area designated
nonattainment for the 2012 annual
PM2.5 NAAQS. The ICL comment letter
concludes that the control measures and
associated emissions reductions are not
permanent nor enforceable.
Response—We disagree with the
commenter. Measures to attain the 24hour PM10 NAAQS were submitted by
IDEQ on April 14, 1992, and approved
into the SIP on August 25, 1994 (59 FR
43745). In the August 25, 1994 action,
the EPA evaluated the IDEQ’s submittal
with respect to the CAA section 172
requirements, including the Reasonably
Available Control Measures and their
enforceability. The EPA approved the
control measures into the SIP at 40 CFR
part 52, subpart N as meeting CAA
requirements and making them, along
with the attainment plan itself, federally
enforceable (59 FR 43745). Once
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approved, the state is subject to CAA
section 179(a)(4), which provides that a
state can be subject to federal sanctions
for not implementing any requirement
of an approved plan or part of an
approved plan, unless the deficiency is
corrected within 18 months.
Reviewing the specific plan measures,
the IDEQ has implemented woodstove
replacements and home weatherization
since the early 1990s in the Pinehurst
PM10 NAA. As identified in Table 9 of
the IDEQ submittal, the woodstove
changeout program resulted in 76
uncertified woodstoves being replaced
by 1994, with an additional 87 between
1995 and 2014 and 40 more between
2015 and 2017. These measures have
been implemented through a variety of
programs and agencies. Changeouts of
uncertified woodstoves were completed
through a combined Federal assistance
grant and state and local loan program.
This combined program was
administered by the Northern Idaho
Community Action Agency. The home
weatherization program was run
through the Idaho Economic
Opportunity Office with loan and grant
funding supplied by the Idaho
Department of Water Resources,
Farmers Home Administration,
Washington Water Power, and North
Idaho Community Action Agency. In
terms of emissions reductions, when
comparing the emissions inventories
from residential wood combustion from
1988 to 2013, they dropped 80.25 lb/day
(27.45%) during the winter season when
particulate matter emissions are often
the highest (Table 8 of the IDEQ
submittal). These reductions are
permanent in that both the woodstove
replacement and the reduced energy
needs from improved home energy
efficiency via weatherization generally
last and extend throughout the life of
the home.1 Any subsequent home
modification would likely improve, if
not maintain, emissions reductions, and
benefits are expected to be net positive
given that emissions of EPA-certified
stoves are estimated to be on average
three to four times lower than
uncertified stoves.2 The remaining
measures, including the public
awareness campaign focused on clean
burning practices and the voluntary
woodsmoke curtailment programs are
all helpful in supporting the reduction
of woodsmoke emissions in the area.
Additionally, the EPA recently
awarded IDEQ a 2015 Targeted Airshed
1 See Department of Energy Weatherization
Program, https://www.energy.gov/sites/prod/files/
2018/06/f52/EERE_WAP_Fact%20Sheet-v2.pdf.
2 See EPA Burnwise Program, https://
www.epa.gov/burnwise/burn-wise-energy-efficiency.
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Grant for the West Silver Valley PM2.5
NAA. As a condition of the grant
agreement with the EPA, the IDEQ
committed to replace 183 uncertified
wood heating devices and provide the
associated emissions reductions. Each
homeowner receiving a changeout must
sign a certification document to ensure
that they will remove an uncertified
wood heating device from their home
and agree to have two follow-up home
inspections on the new certified device,
commit to proper wood burning
practices, and commit to not replacing
the device with another solid fuel
burning device. All removed stoves are
rendered permanently and irreversibly
inoperable and are properly disposed.
We believe the grant terms and
conditions and the homeowner
certifications provide additional
enforceability for purposes of
maintaining the PM10 standard in the
area.
While not specifically taken credit for
in the original attainment plan nor the
LMP, road dust control has played an
important part in the area. It is the
second largest source of pollution
according to the emissions inventory,
and the area has taken measures to
reduce emissions through paving roads,
maintenance of roads, and adjusting
street sweeping to reduce particulate
matter. With respect to permanence of
road controls, once paved their
associated emissions will be reduced
and road maintenance will ensure
lasting emissions reductions. We
received clarification from the IDEQ that
since 2016, the majority of roads (over
10 miles in a city roughly 1 square mile)
in the Pinehurst area have been rebuilt
or sealed.
We have reviewed monitoring data for
the area with respect to the permanence
of the emissions reductions. In Table 2
of the IDEQ submittal, monitoring data
is provided from 1986 through 2015.
From 1986 through 1993, the Pinehurst
PM10 NAA was regularly recording
values above 100 mg/m3, and exceeded
the 3-year expected exceedances design
value of 1.0. From 1994 through 2015,
Table 2 shows that the area has
consistently met the 24-hour PM10
standard, and the EPA has reviewed and
confirmed the data. As noted in the
submittal, the area came into attainment
in the same timeframe as the IDEQ’s
completion of the first batch of
woodstove changeouts (76 by 1994). The
area has continued to meet the 24-hour
PM10 NAAQS design value since 1994,
and it has also shown a continued
decrease in maximum annual 24-hr
PM10 concentrations. Additionally, the
EPA has determined that the Pinehurst
PM10 NAA meets the 5-year average
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design value for LMP qualification as
identified in the proposal.
Since the proposal, the IDEQ has
submitted and the EPA has reviewed
and concurred on the IDEQ’s
demonstration that elevated PM10
concentrations on three days in
September 2017 were attributable to
wildfire exceptional events and qualify
for exclusion under EPA’s Exceptional
Events Rule. The August 24, 2018
concurrence letter to the IDEQ is
included in the docket. With the
exceptional event days excluded, the
area continues to meet the LMP average
design value for the most recent 5-year
period, through 2017. The EPA intends
to propose final agency action on these
2017 exceptional events in a
forthcoming action.
Based on the IDEQ PM10 LMP
submission and the EPA’s review of air
quality monitoring data, it is reasonable
to conclude that the measures to reduce
PM10 in the Pinehurst PM10 NAA have
contributed to permanent emissions
reductions. Emissions reductions in the
area have been maintained since 1994,
and enforceable control measures
remain in place as approved into the
SIP. We therefore conclude that the area
has met its obligations with regard to
permanent and enforceable measures to
maintain the 24-hour PM10 standard and
that no further action is required.
Comment—Annual PM10 NAAQS
Summary—The ICL requests that the
EPA explain why the LMP and the
EPA’s subsequent analysis only
evaluated the 24-hour PM10 LMP design
value and not the annual PM10 LMP
design value. The commenter asserts
that both are required.
Response—On August 9, 2001, the
EPA issued guidance on streamlined
maintenance plan provisions for certain
moderate PM10 nonattainment areas
seeking redesignation to attainment
(Memorandum from Lydia Wegman,
Director, Air Quality Standards and
Strategies Division, entitled ‘‘Limited
Maintenance Plan Option for Moderate
PM10 Nonattainment Areas’’ (LMP
Option Memo)). Section IV of the LMP
Option Memo discusses LMP
qualification and qualifying design
values specifically. It states that ‘‘[t]he
area should be attaining the NAAQS
and the average PM10 design value for
the area, based on the most recent 5
years of air quality data at all monitors
in the area, should be at or below 40 mg/
m3 for the annual PM10 NAAQS and 98
mg/m3 for the 24-hr PM10 NAAQS with
no violations at any monitor in the
nonattainment area.’’
To qualify for the LMP option, the
area must meet the design value test
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with respect to the standard for which
the area was designated nonattainment.3
The Pinehurst PM10 NAA was
designated nonattainment for the 24-hr
PM10 NAAQS and therefore the
appropriate statistical test is with
respect to the 98 mg/m3 5-year average
design value. The EPA has confirmed
that the area meets the 5-year average
design value of 98 mg/m3. We believe
that the IDEQ has met the requirements
of the LMP with regards to the 24-hr
PM10 standard and the IDEQ does not
need to address the annual PM10
standard.
Comment—Federal Clean Air
Deregulation
Summary—The ICL states that they
are concerned about recent actions and
statements by federal agencies that may
affect vehicle emissions reductions in
the future, and how that may affect the
Pinehurst PM10 NAA ability to attain
and its permanence. The ICL comment
letter specifically points to the IDEQ’s
reference to Tier 3 vehicle standards
and the EPA’s proposal to reduce
Corporate Average Fuel Economy
(CAFE) standards. The comment then
requests that the EPA ‘‘identify any and
all of its models and analyses that may
be impacted by current and proposed
deregulation of vehicle emissions.
Furthermore, we request that any
vehicle emission model or emission
factor for PM10 be revised such that the
models and factors are not based on any
federal emission regulation currently
under judicial or administrative
review.’’
Response—We do not agree with the
commenter’s assertion regarding the
impact of current or proposed changes
to motor vehicle emissions standards on
the proposed action, because the
Pinehurst PM10 NAA does not rely on
motor vehicle emissions reductions for
attainment or its continued maintenance
of the NAAQS. Additionally, there are
no proposed changes to Tier 3 vehicle
standards and proposed CAFE standards
have minimal effect on criteria
pollutants, their focus instead being on
greenhouse gas emissions reductions.
When reviewing the submitted
Pinehurst PM10 2013 Emissions
Inventory in Table 7 of the IDEQ’s
submittal, the primary source of PM10 is
residential wood combustion at 17.75
tons per year (TPY), which is 44.5% of
the PM10 emissions in the area. Road
dust, paved and unpaved, is the next
largest contributor at a cumulative 8.91
TPY, or 22.3% of emissions.
Cumulatively, residential wood
combustion and road dust make up
3 See
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LMP Option Memo.
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66.8% of the emissions inventory.
During winter days when particulate
matter levels are often higher,
residential wood combustion is 212.05
lb/day, which is 82.17% of the PM10
emissions in the area (Table 8). Paved
road dust (unpaved is no longer part of
the emissions inventory), is the next
largest contributor at a 25.38 lb/day, or
9.83% of emissions. Residential wood
combustion currently makes up the
majority of the emissions inventory.
Motor vehicle emissions by comparison
make up a very small portion of the
emissions inventory at 1.84
TPY(annual) and 11.09 lb/day(winter),
or less than 5% of both the annual and
winter emissions inventories. This is
expected as motor vehicle emissions do
not contribute large quantities of PM10.
As described in section 3.4 Control
Measures and section 3.2.2 Emissions
Inventory Results and Adequacy
Determination, the Pinehurst PM10 LMP
focuses primarily on the reduction of
PM10 emissions from residential
woodsmoke and from road dust from
paved and unpaved roads. The
Pinehurst PM10 LMP itself does not take
credit for emissions reductions from
motor vehicle emissions reductions nor
does it rely on it for continued
attainment of the PM10 NAAQS.
As mentioned in the proposal, the
Pinehurst area has met the PM10 3-year
design value of expected exceedance of
1.0 or less since 1994. Additionally, the
Pinehurst area has only recorded one
value (in 2010) above 98 mg/m3 since
1999 that was not the result of an
exceptional event. The area has
demonstrated, and EPA has confirmed,
that the 3-yr and 5-yr design values
qualify for the LMP option.
Additionally, the area has demonstrated
that it meets the LMP motor vehicle
regional analysis, which assesses
increases in emissions based on the
area’s growth rate as applied to paved
road dust emissions, unpaved road dust
emissions, and mobile source emissions.
It is this last category where the ICL
comment questions if any changes in
federal emissions requirements would
affect the area’s ability to attain. As
explained above, motor vehicle
emissions in the Pinehurst NAA are not
expected to affect the areas ability to
continue to attain as they are less than
5% and were not taken credit for in the
attainment plan, nor the redesignation
request and LMP.
While we do not believe that any
changes to motor vehicle emissions are
relevant to the area’s ability to attain, we
did a basic evaluation to determine if
the area would continue to meet the
LMP motor vehicle regional analysis.
The only portion of the calculation that
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would change would be the on-road
mobile source. Currently, that value is
calculated using the formula in the LMP
Option Memo: DV mobile * VMT paved,
where the DV mobile provides a 3.6509
mg/m3 contribution to the design value
and VMT paved is the 0.0166 percent
growth rate (3.6509 * 0.0166 = 0.06 mg/
m3 contribution). Given that the growth
rate in Pinehurst is very small, any
potential changes to the emissions
standards would have a small effect on
the design value. Taking a conservative
assumption and doubling the DV mobile
from 3.6509 mg/m3 to 7.3018 mg/m3, and
applying the 0.0166 growth rate would
only increase the mobile contribution
from 0.06 mg/m3 contribution to 0.12 mg/
m3 contribution and the Pinehurst area
would still be able meet the motor
vehicle regional analysis test. Given the
small contribution of motor vehicle
emissions and low growth rate in the
Pinehurst area, we believe the Pinehurst
PM10 NAA LMP is sufficient and no
further action is required.
The ICL’s request that the EPA
identify and revise all of its models,
analyses, and emissions factors that may
be impacted by current or proposed
changes to vehicle emissions standards
is outside of the scope of this action.
Comment—Emission Factors
Summary—The ICL requested that the
EPA confirm that all woodstoves
replaced were ‘‘Phase II,’’ and to require
that the IDEQ revise calculations in the
case that any of the replacements were
not Phase II. The ICL asserts that the
IDEQ used incorrect emissions factors
based on a comparison of AP–42
emissions factors to those used by IDEQ
in the Pinehurst PM10 LMP, and
requests an explanation for this or
revision, whichever is more appropriate.
Response—We disagree that the IDEQ
used incorrect emissions factors and do
not believe that any further calculations
are needed. In 1988, the EPA finalized
the residential wood heaters new source
performance standards (NSPS) that
required performance standards for
woodstoves. These performance
standards were released in two phases;
Phase I went into effect immediately in
1988, and Phase II went into effect in
1990. The Phase II performance
standards required that catalytic stoves
have an emission rate of 4.1g/hr or less
and non-catalytic stoves have an
emissions rate of 7.5 g/hr or less. All
stoves that have been replaced in
Pinehurst occurred after Phase II
standards were in place. Additionally,
we have received confirmation from
IDEQ that these changeouts were
completed and that they were Phase II
EPA certified stoves.
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With regard to the ICL’s request for
explanation of the emissions factors
used, we reviewed the emissions factors
(EFs) for residential wood combustion
that IDEQ used and found them
consistent with the EPA EFs and
methodology used in the 2014 National
Emissions Inventory. The IDEQ used
EFs derived from EPA’s Residential
Wood Combustion Emissions
Estimation Tool version 3.1 (October
2016) that are more up to date than the
EFs in AP–42, which were last updated
in 1996 for this source category. We
have included in the docket the
documentation for v3.1 and 3.2 of the
Residential Wood Combustion
Emissions Estimation Tool, which has
the emissions factors used and the
references for those EFs. Both versions
of the tool use the same EFs.
In response to the comment, we have
confirmed with the IDEQ that the
changeouts were with phase II or better
EPA certified stoves. We have also
confirmed that the IDEQ emissions
inventory assumptions and calculations
are correct and that the appropriate EFs
were used.
Comment—Contingency Plan
Summary—The ICL requested that the
EPA further explain how the IDEQ’s
Contingency Plan is compliant with
section 175A of the CAA. The comment
provides a summary with references to
CAA section 175A, the Calcagni Memo
that provides guidance for maintenance
plans, and the LMP Option Memo that
provides guidance for LMPs.
Response—While the commenter
correctly identifies that CAA section
175A provides the statutory
requirements for maintenance plan
requirements, and that the LMP Option
Memo provides guidance for
contingency provisions under the LMP
option, the ICL’s contention that
contingency provisions 4 must be fully
adopted and take effect within one year
and without further legislative action is
incorrect. These requirements do not
appear in the CAA section 175A
requirements nor the LMP Option
Memo, and are contradicted by the
Calcagni Memo, EPA’s long-standing
interpretation of redesignation and
maintenance plan requirements. There,
it states, ‘‘For the purposes of section
175A, a State is not required to have
fully adopted contingency measures that
will take effect without further action by
the State in order for the maintenance
4 The IDEQ submittal and ICL comment letter use
the terminology ‘‘contingency measures,’’ when
referring to the CAA section 175A ‘‘contingency
provisions’’ requirements. ‘‘Contingency measures’’
are associated with attainment planning and have
different requirements.
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plan to be approved.’’ Calcagni Memo at
12; see also Greenbaum v. EPA, 370
F.3d 527, 541 (6th Cir. 2004) (upholding
this portion of the Calcagni Memo).
CAA section 175A(d) and EPA’s
interpretation of that provision as set
out in the Calcagni Memo and the LMP
Option Memo provide the standards by
which the EPA must evaluate
contingency plans. Section 175A(d)
states that ‘‘[e]ach plan revision
submitted under this section shall
contain such contingency provisions as
the Administrator deems necessary to
assure that the State will promptly
correct any violation of the standard
which occurs after the redesignation of
the area as an attainment area. Such
provisions shall include a requirement
that the State will implement all
measures with respect to the control of
the air pollutant concerned which were
contained in the State implementation
plan for the area before redesignation of
the area as an attainment area.’’ The
Calcagni Memo and the LMP Option
memo further elaborate that ‘‘Section
175A of the Act states that a
maintenance plan must include
contingency provisions, as necessary, to
promptly correct any violation of the
NAAQS which may occur after
redesignation of the area to attainment.
These contingency measures do not
have to be fully adopted at the time of
redesignation. However, the
contingency plan is considered to be an
enforceable part of the SIP and the State
should ensure that the contingency
measures are adopted as soon as
possible once they are triggered by a
specific event. The contingency plan
should identify the measures to be
adopted, and provide a schedule and
procedure for adoption and
implementation of the measures if they
are required. Normally, the
implementation of contingency
measures is triggered by a violation of
the NAAQS but the State may wish to
establish other triggers to prevent a
violation of the NAAQS, such as an
exceedance of the NAAQS.’’
The EPA has determined that the
IDEQ’s contingency plan meets the
requirements of Section 175A(d) and the
EPA’s guidance memos. Section 3.5 of
the IDEQ’s submittal confirms that all
measures relied upon for attainment,
including woodstove changeouts,
voluntary curtailment program, home
weatherization, and public awareness
campaign continue to be in place and
will be strengthened if the PM10
standard is exceeded. If the Pinehurst
area exceeds the standard, Section 3.5.1
identifies the Annual Network Plan
monitoring data as the triggering
mechanism for contingency provisions.
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A violation cited in the Annual Network
Plan would trigger a schedule and
process for IDEQ to examine the data,
assess the source of the problem, and
identify which contingency provision to
adopt and implement. The submitted
plan lists potential provisions focused
on control of woodsmoke and road dust,
the two primary sources of PM10 in the
nonattainment area. The submitted
contingency provisions meet the CAA
section 175A requirement to continue
implementing measures relied upon for
attainment. There is an automatic
process on a set schedule by which the
Pinehurst area’s design value is
evaluated annually (i.e., the Annual
Network Plan submittal-reviewapproval), and a violation would trigger
the state to be required to evaluate,
identify, adopt, and implement
contingency provisions best suited
towards bringing the area back into
attainment. Therefore, the EPA is
finalizing approval of the IDEQ’s plan as
meeting the requirements of section
175A.
III. Final Action
The EPA is approving the Pinehurst
PM10 NAA LMP submitted by the IDEQ
and concurrently redesignating the area
to attainment for the PM10 NAAQS.
Related to this action, the EPA is taking
final agency action on the September 15,
2013, high wind exceptional event at
the Pinehurst monitoring station.
Additionally, the EPA is approving the
West Silver Valley annual PM2.5 base
year emissions inventory as meeting
CAA section 172(c)(3) requirements.
IV. Statutory and Executive Orders
Review
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
Act and applicable federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions, the
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• is not an Executive Order 13771 (82
FR 9339, February 2, 2017) regulatory
action because SIP approvals are
exempted under Executive Order 12866;
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• does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the Clean Air Act;
and
• does not provide the EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
The SIP is not approved to apply on
any Indian reservation land or in any
other area where the EPA or an Indian
tribe has demonstrated that a tribe has
jurisdiction. In those areas of Indian
country, the rule does not have tribal
implications and it 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).
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing this action
and other required information to the
U.S. Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This action is not a
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‘‘major rule’’ as defined by 5 U.S.C.
804(2).
Under section 307(b)(1) of the CAA,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the appropriate
circuit by November 13, 2018. Filing a
petition for reconsideration by the
Administrator of this final rule does not
affect the finality of this action for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review may be filed, and
shall not postpone the effectiveness of
such rule or action. This action may not
be challenged later in proceedings to
enforce its requirements. (See section
307(b)(2)).
List of Subjects
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Nitrogen dioxide, Particulate matter,
Reporting and recordkeeping
requirements, Sulfur dioxide.
■
40 CFR Part 81
Environmental protection, Air
pollution control, National parks,
Wilderness areas.
■
1. The authority citation for part 52
continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart N—Idaho
2. In § 52.670, the table in paragraph
(e) is amended by adding an entry at the
end of the table for ‘‘Pinehurst PM10
Limited Maintenance Plan’’ to read as
follows:
Authority: 42 U.S.C. 7401 et seq.
Dated: August 30, 2018.
Michelle L. Pirzadeh,
Acting Regional Administrator, Region 10.
§ 52.670
*
For the reasons set forth in the
preamble, 40 CFR parts 52 and 81 are
amended as follows:
Identification of plan.
*
*
(e) * * *
*
*
EPA-APPROVED IDAHO NONREGULATORY PROVISIONS AND QUASI-REGULATORY MEASURES
State
submittal
date
Name of SIP
provision
Applicable geographic or
nonattainment area
*
*
Pinehurst PM10 Limited Maintenance Plan.
*
*
Shoshone County; Pinehurst Expansion Area and City of Pinehurst.
PART 81—DESIGNATION OF AREAS
FOR AIR QUALITY PLANNING
PURPOSES
3. The authority citation for part 81
continues to read as follows:
■
EPA approval date
Comments
*
*
9/11/2018, ......................................
[Insert Federal Register citation] ..
9/29/2017
Authority: 42 U.S.C. 7401 et seq.
4. In § 81.313, the table entitled
‘‘Idaho-PM–10’’ is amended by revising
the entry for ‘‘Eastern Washington-
■
*
Northern Idaho Interstate AQCR 62
(Idaho portion):’’ to read as follows:
§ 81.313
*
Idaho.
*
*
*
*
IDAHO PM–10
Designation
Classification
Designated area
Date
*
*
*
Eastern Washington-Northern Idaho Interstate AQCR 62 (Idaho portion):
Shoshone County: Pinehurst Expansion Area Northwest quarter of the
Northwest quarter, Section 8, Township 48 North, Range 2 East; Southwest quarter of the Northwest quarter, Section 8, Township 48, North,
Range 2 East; Northwest quarter of the Southwest quarter, Section 8,
Township 48 North, Range 2 East; Southwest quarter, Section 8, Township 48 North, Range 2 East; Southwest quarter of the Southwest quarter, Section 48 North, Range 2 East, Boise Base (known as ‘‘Pinehurst
expansion area’’).
City of Pinehurst ..............................................................................................
*
*
*
*
*
*
*
Type
Date
*
*
*
October 11, 2018
Attainment ............
..............................
October 11, 2018
Attainment ............
..............................
*
*
*
*
*
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Agencies
[Federal Register Volume 83, Number 176 (Tuesday, September 11, 2018)]
[Rules and Regulations]
[Pages 45830-45835]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-19600]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[EPA-R10-OAR-2017-0582; FRL-9983-53--Region 10]
Air Plan Approval; ID, Pinehurst PM10 Redesignation,
Limited Maintenance Plan; West Silver Valley 2012 Annual
PM2.5 Emission Inventory
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The EPA is approving the redesignation request and limited
maintenance plan for the PM10 National Ambient Air Quality
Standard developed for the City of Pinehurst PM10
Nonattainment Area and the Pinehurst PM10 Expansion
Nonattainment Area. This redesignation will change the status of both
areas from nonattainment to attainment. The limited maintenance plan
for these contiguous nonattainment areas addresses maintenance of the
PM10 standard for a ten-year period beyond redesignation.
Related to this action, the EPA is taking final agency action on the
September 15, 2013, high wind exceptional event at the Pinehurst
monitoring station. Additionally, the EPA is finalizing approval of the
emissions inventory for the West Silver Valley 2012 annual
PM2.5 nonattainment area.
DATES: This action is effective on October 11, 2018.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-R10-OAR-2017-0582. All documents in the docket are
listed on the https://www.regulations.gov website. Although listed in
the index, some information is not publicly available, e.g.,
Confidential Business Information or other information the disclosure
of which is restricted by statute. Certain other material, such as
copyrighted material, is not placed on the internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available through https://www.regulations.gov, or please
contact the person identified in the For Further Information Contact
section for additional availability information.
FOR FURTHER INFORMATION CONTACT: Justin Spenillo at (206) 553-6125, or
[email protected].
SUPPLEMENTARY INFORMATION: Throughout this document whenever ``we,''
``us,'' or ``our'' is used, it is intended to refer to the EPA.
Table of Contents
I. Background Information
II. Response to Comments
III. Final Action
IV. Statutory and Executive Orders Review
I. Background Information
On May 11, 2018, the EPA proposed to approve the redesignation
request and limited maintenance plan (LMP) submitted by the Idaho
Department of Environmental Quality (IDEQ) on September 29, 2017, for
the City of Pinehurst PM10 Nonattainment Area and the
Pinehurst PM10 Expansion Nonattainment Area, collectively
referred to as the Pinehurst PM10 Nonattainment Area
(Pinehurst PM10 NAA).
Related to this action, the EPA is taking final agency action on
the EPA's concurrence with the IDEQ's request for
[[Page 45831]]
exclusion of data measured on September 15, 2013, as a high wind
exceptional event at the Pinehurst monitoring station, as set forth in
the March 2, 2017 letter to the IDEQ, included in the docket. The Clean
Air Act (CAA) allows for the exclusion of air quality monitoring data
from design value calculations when there are exceedances caused by
events, such as wildfires or high wind events, that meet the criteria
for an exceptional event identified in the EPA's implementing
regulations, the Exceptional Events Rule at 40 CFR 50.1, 50.14 and
51.930. In 2013, emissions from a high wind event entrained dust and
impacted PM10 concentrations recorded at the Pinehurst
monitor. The EPA evaluated the IDEQ's exceptional event demonstration
for the flagged values of the 24-hour PM10 NAAQS for
September 15, 2013, at the monitor in Pinehurst, Idaho, with respect to
the requirements of the EPA's Exceptional Events Rule and determined
that IDEQ met the rule requirements.
Separately, the EPA also proposed approval of the base year
emissions inventory for the West Silver Valley (WSV) PM2.5
Nonattainment Area (NAA). Section 172(c)(3) of the CAA requires a state
with an area designated as nonattainment to submit a ``comprehensive,
accurate, current inventory of actual emissions from all sources of the
relevant pollutant'' for the NAA. The IDEQ developed a 2013 base year
emissions inventory for the WSV annual PM2.5 NAA. The base
year emissions inventory includes data from 2013 and 2014 and in large
part was extracted from the 2014 periodic emissions inventory which is
used to populate the EPA's National Emissions Inventory. The 2013 base
year inventory is one of the three years used to designate the area as
nonattainment. This base year inventory presents direct
PM2.5 emissions (condensable and filterable) and emissions
of all PM2.5 precursors (NOX, VOCs,
NH3, and SO2) to meet the emissions inventory
requirements of CAA section 172(c)(3) and 40 CFR 51.1008(a)(1). The EPA
has reviewed the results, procedures, and methodologies for the WSV
Annual PM2.5 NAA base year emissions inventory. The EPA
determined that the 2013 base year emissions inventory for the WSV
annual PM2.5 NAA met the requirements of CAA section
172(c)(3) and 40 CFR 51.1008(a)(1).
An explanation of the CAA requirements, a detailed analysis of the
submittal, and the EPA's reasons for proposing approval were provided
in the notice of proposed rulemaking (83 FR 21976), and will not be
restated here. The public comment period for this proposed rule ended
on June 11, 2018. The EPA received adverse comments on the proposal.
II. Response to Comments
The Idaho Conservation League (ICL) submitted adverse comments on
our proposed approval of the Pinehurst PM10 NAA
redesignation request and LMP. Within this section, we have summarized
the adverse comments and provided our responses. A full copy of
comments received is available in the docket for this final action.
Comment--Permanent and Enforceable Emissions Reductions
Summary--The ICL comment letter asserts the ``EPA must reject Idaho
DEQ's request for redesignation of the Pinehurst NAA'' because the
state has not met the redesignation requirements in CAA section
107(d)(3)(E)(iii). The ICL cites the EPA's September 4, 1992, guidance,
which, among other things, addresses emissions reductions based on
permanent and enforceable measures (Memorandum from John Calcagni,
Director, Air Quality Management Division, EPA Office of Air Quality
Planning and Standards, entitled ``Procedures for Processing Requests
to Redesignate Areas to Attainment'' (Calcagni Memo)). The ICL comment
letter provides examples of nonattainment areas redesignated for
PM10 and ozone in Ohio, Colorado, and Idaho, which use local
rules, laws, and ordinances to provide for permanent and enforceable
emissions reductions. The comment letter states that the IDEQ and City
of Pinehurst were aware of the need for permanent and enforceable
measures, citing discussion notes taken during a 2016 advisory
committee session for the West Silver Valley PM2.5 NAA, an
overlapping area designated nonattainment for the 2012 annual
PM2.5 NAAQS. The ICL comment letter concludes that the
control measures and associated emissions reductions are not permanent
nor enforceable.
Response--We disagree with the commenter. Measures to attain the
24-hour PM10 NAAQS were submitted by IDEQ on April 14, 1992,
and approved into the SIP on August 25, 1994 (59 FR 43745). In the
August 25, 1994 action, the EPA evaluated the IDEQ's submittal with
respect to the CAA section 172 requirements, including the Reasonably
Available Control Measures and their enforceability. The EPA approved
the control measures into the SIP at 40 CFR part 52, subpart N as
meeting CAA requirements and making them, along with the attainment
plan itself, federally enforceable (59 FR 43745). Once approved, the
state is subject to CAA section 179(a)(4), which provides that a state
can be subject to federal sanctions for not implementing any
requirement of an approved plan or part of an approved plan, unless the
deficiency is corrected within 18 months.
Reviewing the specific plan measures, the IDEQ has implemented
woodstove replacements and home weatherization since the early 1990s in
the Pinehurst PM10 NAA. As identified in Table 9 of the IDEQ
submittal, the woodstove changeout program resulted in 76 uncertified
woodstoves being replaced by 1994, with an additional 87 between 1995
and 2014 and 40 more between 2015 and 2017. These measures have been
implemented through a variety of programs and agencies. Changeouts of
uncertified woodstoves were completed through a combined Federal
assistance grant and state and local loan program. This combined
program was administered by the Northern Idaho Community Action Agency.
The home weatherization program was run through the Idaho Economic
Opportunity Office with loan and grant funding supplied by the Idaho
Department of Water Resources, Farmers Home Administration, Washington
Water Power, and North Idaho Community Action Agency. In terms of
emissions reductions, when comparing the emissions inventories from
residential wood combustion from 1988 to 2013, they dropped 80.25 lb/
day (27.45%) during the winter season when particulate matter emissions
are often the highest (Table 8 of the IDEQ submittal). These reductions
are permanent in that both the woodstove replacement and the reduced
energy needs from improved home energy efficiency via weatherization
generally last and extend throughout the life of the home.\1\ Any
subsequent home modification would likely improve, if not maintain,
emissions reductions, and benefits are expected to be net positive
given that emissions of EPA-certified stoves are estimated to be on
average three to four times lower than uncertified stoves.\2\ The
remaining measures, including the public awareness campaign focused on
clean burning practices and the voluntary woodsmoke curtailment
programs are all helpful in supporting the reduction of woodsmoke
emissions in the area.
---------------------------------------------------------------------------
\1\ See Department of Energy Weatherization Program, https://www.energy.gov/sites/prod/files/2018/06/f52/EERE_WAP_Fact%20Sheet-v2.pdf.
\2\ See EPA Burnwise Program, https://www.epa.gov/burnwise/burn-wise-energy-efficiency.
---------------------------------------------------------------------------
Additionally, the EPA recently awarded IDEQ a 2015 Targeted Airshed
[[Page 45832]]
Grant for the West Silver Valley PM2.5 NAA. As a condition
of the grant agreement with the EPA, the IDEQ committed to replace 183
uncertified wood heating devices and provide the associated emissions
reductions. Each homeowner receiving a changeout must sign a
certification document to ensure that they will remove an uncertified
wood heating device from their home and agree to have two follow-up
home inspections on the new certified device, commit to proper wood
burning practices, and commit to not replacing the device with another
solid fuel burning device. All removed stoves are rendered permanently
and irreversibly inoperable and are properly disposed. We believe the
grant terms and conditions and the homeowner certifications provide
additional enforceability for purposes of maintaining the
PM10 standard in the area.
While not specifically taken credit for in the original attainment
plan nor the LMP, road dust control has played an important part in the
area. It is the second largest source of pollution according to the
emissions inventory, and the area has taken measures to reduce
emissions through paving roads, maintenance of roads, and adjusting
street sweeping to reduce particulate matter. With respect to
permanence of road controls, once paved their associated emissions will
be reduced and road maintenance will ensure lasting emissions
reductions. We received clarification from the IDEQ that since 2016,
the majority of roads (over 10 miles in a city roughly 1 square mile)
in the Pinehurst area have been rebuilt or sealed.
We have reviewed monitoring data for the area with respect to the
permanence of the emissions reductions. In Table 2 of the IDEQ
submittal, monitoring data is provided from 1986 through 2015. From
1986 through 1993, the Pinehurst PM10 NAA was regularly
recording values above 100 [micro]g/m\3\, and exceeded the 3-year
expected exceedances design value of 1.0. From 1994 through 2015, Table
2 shows that the area has consistently met the 24-hour PM10
standard, and the EPA has reviewed and confirmed the data. As noted in
the submittal, the area came into attainment in the same timeframe as
the IDEQ's completion of the first batch of woodstove changeouts (76 by
1994). The area has continued to meet the 24-hour PM10 NAAQS
design value since 1994, and it has also shown a continued decrease in
maximum annual 24-hr PM10 concentrations. Additionally, the
EPA has determined that the Pinehurst PM10 NAA meets the 5-
year average design value for LMP qualification as identified in the
proposal.
Since the proposal, the IDEQ has submitted and the EPA has reviewed
and concurred on the IDEQ's demonstration that elevated PM10
concentrations on three days in September 2017 were attributable to
wildfire exceptional events and qualify for exclusion under EPA's
Exceptional Events Rule. The August 24, 2018 concurrence letter to the
IDEQ is included in the docket. With the exceptional event days
excluded, the area continues to meet the LMP average design value for
the most recent 5-year period, through 2017. The EPA intends to propose
final agency action on these 2017 exceptional events in a forthcoming
action.
Based on the IDEQ PM10 LMP submission and the EPA's
review of air quality monitoring data, it is reasonable to conclude
that the measures to reduce PM10 in the Pinehurst
PM10 NAA have contributed to permanent emissions reductions.
Emissions reductions in the area have been maintained since 1994, and
enforceable control measures remain in place as approved into the SIP.
We therefore conclude that the area has met its obligations with regard
to permanent and enforceable measures to maintain the 24-hour
PM10 standard and that no further action is required.
Comment--Annual PM10 NAAQS
Summary--The ICL requests that the EPA explain why the LMP and the
EPA's subsequent analysis only evaluated the 24-hour PM10
LMP design value and not the annual PM10 LMP design value.
The commenter asserts that both are required.
Response--On August 9, 2001, the EPA issued guidance on streamlined
maintenance plan provisions for certain moderate PM10
nonattainment areas seeking redesignation to attainment (Memorandum
from Lydia Wegman, Director, Air Quality Standards and Strategies
Division, entitled ``Limited Maintenance Plan Option for Moderate
PM10 Nonattainment Areas'' (LMP Option Memo)). Section IV of
the LMP Option Memo discusses LMP qualification and qualifying design
values specifically. It states that ``[t]he area should be attaining
the NAAQS and the average PM10 design value for the area,
based on the most recent 5 years of air quality data at all monitors in
the area, should be at or below 40 [mu]g/m\3\ for the annual
PM10 NAAQS and 98 [mu]g/m\3\ for the 24-hr PM10
NAAQS with no violations at any monitor in the nonattainment area.''
To qualify for the LMP option, the area must meet the design value
test with respect to the standard for which the area was designated
nonattainment.\3\ The Pinehurst PM10 NAA was designated
nonattainment for the 24-hr PM10 NAAQS and therefore the
appropriate statistical test is with respect to the 98 [micro]g/m\3\ 5-
year average design value. The EPA has confirmed that the area meets
the 5-year average design value of 98 [micro]g/m\3\. We believe that
the IDEQ has met the requirements of the LMP with regards to the 24-hr
PM10 standard and the IDEQ does not need to address the
annual PM10 standard.
---------------------------------------------------------------------------
\3\ See LMP Option Memo.
---------------------------------------------------------------------------
Comment--Federal Clean Air Deregulation
Summary--The ICL states that they are concerned about recent
actions and statements by federal agencies that may affect vehicle
emissions reductions in the future, and how that may affect the
Pinehurst PM10 NAA ability to attain and its permanence. The
ICL comment letter specifically points to the IDEQ's reference to Tier
3 vehicle standards and the EPA's proposal to reduce Corporate Average
Fuel Economy (CAFE) standards. The comment then requests that the EPA
``identify any and all of its models and analyses that may be impacted
by current and proposed deregulation of vehicle emissions. Furthermore,
we request that any vehicle emission model or emission factor for
PM10 be revised such that the models and factors are not
based on any federal emission regulation currently under judicial or
administrative review.''
Response--We do not agree with the commenter's assertion regarding
the impact of current or proposed changes to motor vehicle emissions
standards on the proposed action, because the Pinehurst PM10
NAA does not rely on motor vehicle emissions reductions for attainment
or its continued maintenance of the NAAQS. Additionally, there are no
proposed changes to Tier 3 vehicle standards and proposed CAFE
standards have minimal effect on criteria pollutants, their focus
instead being on greenhouse gas emissions reductions.
When reviewing the submitted Pinehurst PM10 2013
Emissions Inventory in Table 7 of the IDEQ's submittal, the primary
source of PM10 is residential wood combustion at 17.75 tons
per year (TPY), which is 44.5% of the PM10 emissions in the
area. Road dust, paved and unpaved, is the next largest contributor at
a cumulative 8.91 TPY, or 22.3% of emissions. Cumulatively, residential
wood combustion and road dust make up
[[Page 45833]]
66.8% of the emissions inventory. During winter days when particulate
matter levels are often higher, residential wood combustion is 212.05
lb/day, which is 82.17% of the PM10 emissions in the area
(Table 8). Paved road dust (unpaved is no longer part of the emissions
inventory), is the next largest contributor at a 25.38 lb/day, or 9.83%
of emissions. Residential wood combustion currently makes up the
majority of the emissions inventory. Motor vehicle emissions by
comparison make up a very small portion of the emissions inventory at
1.84 TPY(annual) and 11.09 lb/day(winter), or less than 5% of both the
annual and winter emissions inventories. This is expected as motor
vehicle emissions do not contribute large quantities of
PM10.
As described in section 3.4 Control Measures and section 3.2.2
Emissions Inventory Results and Adequacy Determination, the Pinehurst
PM10 LMP focuses primarily on the reduction of
PM10 emissions from residential woodsmoke and from road dust
from paved and unpaved roads. The Pinehurst PM10 LMP itself
does not take credit for emissions reductions from motor vehicle
emissions reductions nor does it rely on it for continued attainment of
the PM10 NAAQS.
As mentioned in the proposal, the Pinehurst area has met the
PM10 3-year design value of expected exceedance of 1.0 or
less since 1994. Additionally, the Pinehurst area has only recorded one
value (in 2010) above 98 [micro]g/m\3\ since 1999 that was not the
result of an exceptional event. The area has demonstrated, and EPA has
confirmed, that the 3-yr and 5-yr design values qualify for the LMP
option. Additionally, the area has demonstrated that it meets the LMP
motor vehicle regional analysis, which assesses increases in emissions
based on the area's growth rate as applied to paved road dust
emissions, unpaved road dust emissions, and mobile source emissions. It
is this last category where the ICL comment questions if any changes in
federal emissions requirements would affect the area's ability to
attain. As explained above, motor vehicle emissions in the Pinehurst
NAA are not expected to affect the areas ability to continue to attain
as they are less than 5% and were not taken credit for in the
attainment plan, nor the redesignation request and LMP.
While we do not believe that any changes to motor vehicle emissions
are relevant to the area's ability to attain, we did a basic evaluation
to determine if the area would continue to meet the LMP motor vehicle
regional analysis. The only portion of the calculation that would
change would be the on-road mobile source. Currently, that value is
calculated using the formula in the LMP Option Memo: DV mobile * VMT
paved, where the DV mobile provides a 3.6509 [mu]g/m\3\ contribution to
the design value and VMT paved is the 0.0166 percent growth rate
(3.6509 * 0.0166 = 0.06 [mu]g/m\3\ contribution). Given that the growth
rate in Pinehurst is very small, any potential changes to the emissions
standards would have a small effect on the design value. Taking a
conservative assumption and doubling the DV mobile from 3.6509 [mu]g/
m\3\ to 7.3018 [mu]g/m\3\, and applying the 0.0166 growth rate would
only increase the mobile contribution from 0.06 [micro]g/m\3\
contribution to 0.12 [micro]g/m\3\ contribution and the Pinehurst area
would still be able meet the motor vehicle regional analysis test.
Given the small contribution of motor vehicle emissions and low growth
rate in the Pinehurst area, we believe the Pinehurst PM10
NAA LMP is sufficient and no further action is required.
The ICL's request that the EPA identify and revise all of its
models, analyses, and emissions factors that may be impacted by current
or proposed changes to vehicle emissions standards is outside of the
scope of this action.
Comment--Emission Factors
Summary--The ICL requested that the EPA confirm that all woodstoves
replaced were ``Phase II,'' and to require that the IDEQ revise
calculations in the case that any of the replacements were not Phase
II. The ICL asserts that the IDEQ used incorrect emissions factors
based on a comparison of AP-42 emissions factors to those used by IDEQ
in the Pinehurst PM10 LMP, and requests an explanation for
this or revision, whichever is more appropriate.
Response--We disagree that the IDEQ used incorrect emissions
factors and do not believe that any further calculations are needed. In
1988, the EPA finalized the residential wood heaters new source
performance standards (NSPS) that required performance standards for
woodstoves. These performance standards were released in two phases;
Phase I went into effect immediately in 1988, and Phase II went into
effect in 1990. The Phase II performance standards required that
catalytic stoves have an emission rate of 4.1g/hr or less and non-
catalytic stoves have an emissions rate of 7.5 g/hr or less. All stoves
that have been replaced in Pinehurst occurred after Phase II standards
were in place. Additionally, we have received confirmation from IDEQ
that these changeouts were completed and that they were Phase II EPA
certified stoves.
With regard to the ICL's request for explanation of the emissions
factors used, we reviewed the emissions factors (EFs) for residential
wood combustion that IDEQ used and found them consistent with the EPA
EFs and methodology used in the 2014 National Emissions Inventory. The
IDEQ used EFs derived from EPA's Residential Wood Combustion Emissions
Estimation Tool version 3.1 (October 2016) that are more up to date
than the EFs in AP-42, which were last updated in 1996 for this source
category. We have included in the docket the documentation for v3.1 and
3.2 of the Residential Wood Combustion Emissions Estimation Tool, which
has the emissions factors used and the references for those EFs. Both
versions of the tool use the same EFs.
In response to the comment, we have confirmed with the IDEQ that
the changeouts were with phase II or better EPA certified stoves. We
have also confirmed that the IDEQ emissions inventory assumptions and
calculations are correct and that the appropriate EFs were used.
Comment--Contingency Plan
Summary--The ICL requested that the EPA further explain how the
IDEQ's Contingency Plan is compliant with section 175A of the CAA. The
comment provides a summary with references to CAA section 175A, the
Calcagni Memo that provides guidance for maintenance plans, and the LMP
Option Memo that provides guidance for LMPs.
Response--While the commenter correctly identifies that CAA section
175A provides the statutory requirements for maintenance plan
requirements, and that the LMP Option Memo provides guidance for
contingency provisions under the LMP option, the ICL's contention that
contingency provisions \4\ must be fully adopted and take effect within
one year and without further legislative action is incorrect. These
requirements do not appear in the CAA section 175A requirements nor the
LMP Option Memo, and are contradicted by the Calcagni Memo, EPA's long-
standing interpretation of redesignation and maintenance plan
requirements. There, it states, ``For the purposes of section 175A, a
State is not required to have fully adopted contingency measures that
will take effect without further action by the State in order for the
maintenance
[[Page 45834]]
plan to be approved.'' Calcagni Memo at 12; see also Greenbaum v. EPA,
370 F.3d 527, 541 (6th Cir. 2004) (upholding this portion of the
Calcagni Memo).
---------------------------------------------------------------------------
\4\ The IDEQ submittal and ICL comment letter use the
terminology ``contingency measures,'' when referring to the CAA
section 175A ``contingency provisions'' requirements. ``Contingency
measures'' are associated with attainment planning and have
different requirements.
---------------------------------------------------------------------------
CAA section 175A(d) and EPA's interpretation of that provision as
set out in the Calcagni Memo and the LMP Option Memo provide the
standards by which the EPA must evaluate contingency plans. Section
175A(d) states that ``[e]ach plan revision submitted under this section
shall contain such contingency provisions as the Administrator deems
necessary to assure that the State will promptly correct any violation
of the standard which occurs after the redesignation of the area as an
attainment area. Such provisions shall include a requirement that the
State will implement all measures with respect to the control of the
air pollutant concerned which were contained in the State
implementation plan for the area before redesignation of the area as an
attainment area.'' The Calcagni Memo and the LMP Option memo further
elaborate that ``Section 175A of the Act states that a maintenance plan
must include contingency provisions, as necessary, to promptly correct
any violation of the NAAQS which may occur after redesignation of the
area to attainment. These contingency measures do not have to be fully
adopted at the time of redesignation. However, the contingency plan is
considered to be an enforceable part of the SIP and the State should
ensure that the contingency measures are adopted as soon as possible
once they are triggered by a specific event. The contingency plan
should identify the measures to be adopted, and provide a schedule and
procedure for adoption and implementation of the measures if they are
required. Normally, the implementation of contingency measures is
triggered by a violation of the NAAQS but the State may wish to
establish other triggers to prevent a violation of the NAAQS, such as
an exceedance of the NAAQS.''
The EPA has determined that the IDEQ's contingency plan meets the
requirements of Section 175A(d) and the EPA's guidance memos. Section
3.5 of the IDEQ's submittal confirms that all measures relied upon for
attainment, including woodstove changeouts, voluntary curtailment
program, home weatherization, and public awareness campaign continue to
be in place and will be strengthened if the PM10 standard is
exceeded. If the Pinehurst area exceeds the standard, Section 3.5.1
identifies the Annual Network Plan monitoring data as the triggering
mechanism for contingency provisions. A violation cited in the Annual
Network Plan would trigger a schedule and process for IDEQ to examine
the data, assess the source of the problem, and identify which
contingency provision to adopt and implement. The submitted plan lists
potential provisions focused on control of woodsmoke and road dust, the
two primary sources of PM10 in the nonattainment area. The
submitted contingency provisions meet the CAA section 175A requirement
to continue implementing measures relied upon for attainment. There is
an automatic process on a set schedule by which the Pinehurst area's
design value is evaluated annually (i.e., the Annual Network Plan
submittal-review-approval), and a violation would trigger the state to
be required to evaluate, identify, adopt, and implement contingency
provisions best suited towards bringing the area back into attainment.
Therefore, the EPA is finalizing approval of the IDEQ's plan as meeting
the requirements of section 175A.
III. Final Action
The EPA is approving the Pinehurst PM10 NAA LMP
submitted by the IDEQ and concurrently redesignating the area to
attainment for the PM10 NAAQS. Related to this action, the
EPA is taking final agency action on the September 15, 2013, high wind
exceptional event at the Pinehurst monitoring station. Additionally,
the EPA is approving the West Silver Valley annual PM2.5
base year emissions inventory as meeting CAA section 172(c)(3)
requirements.
IV. Statutory and Executive Orders Review
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the Act and applicable
federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, the EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely approves state law as meeting federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
is not an Executive Order 13771 (82 FR 9339, February 2,
2017) regulatory action because SIP approvals are exempted under
Executive Order 12866;
does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
does not have Federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
is not subject to requirements of Section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the Clean Air Act; and
does not provide the EPA with the discretionary authority
to address, as appropriate, disproportionate human health or
environmental effects, using practicable and legally permissible
methods, under Executive Order 12898 (59 FR 7629, February 16, 1994).
The SIP is not approved to apply on any Indian reservation land or
in any other area where the EPA or an Indian tribe has demonstrated
that a tribe has jurisdiction. In those areas of Indian country, the
rule does not have tribal implications and it 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).
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. The EPA will submit a report containing this action and
other required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A major rule cannot
take effect until 60 days after it is published in the Federal
Register. This action is not a
[[Page 45835]]
``major rule'' as defined by 5 U.S.C. 804(2).
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by November 13, 2018. Filing a petition for
reconsideration by the Administrator of this final rule does not affect
the finality of this action for the purposes of judicial review nor
does it extend the time within which a petition for judicial review may
be filed, and shall not postpone the effectiveness of such rule or
action. This action may not be challenged later in proceedings to
enforce its requirements. (See section 307(b)(2)).
List of Subjects
40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Intergovernmental relations, Nitrogen dioxide, Particulate
matter, Reporting and recordkeeping requirements, Sulfur dioxide.
40 CFR Part 81
Environmental protection, Air pollution control, National parks,
Wilderness areas.
Authority: 42 U.S.C. 7401 et seq.
Dated: August 30, 2018.
Michelle L. Pirzadeh,
Acting Regional Administrator, Region 10.
For the reasons set forth in the preamble, 40 CFR parts 52 and 81
are amended as follows:
PART 52--APPROVAL AND PROMULGATION OF IMPLEMENTATION PLANS
0
1. The authority citation for part 52 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart N--Idaho
0
2. In Sec. 52.670, the table in paragraph (e) is amended by adding an
entry at the end of the table for ``Pinehurst PM10 Limited
Maintenance Plan'' to read as follows:
Sec. 52.670 Identification of plan.
* * * * *
(e) * * *
EPA-Approved Idaho Nonregulatory Provisions and Quasi-Regulatory Measures
----------------------------------------------------------------------------------------------------------------
Applicable
Name of SIP provision geographic or State EPA approval date Comments
nonattainment area submittal date
----------------------------------------------------------------------------------------------------------------
* * * * * * *
Pinehurst PM10 Limited Shoshone County; 9/29/2017 9/11/2018,........ .....................
Maintenance Plan. Pinehurst [Insert Federal
Expansion Area and Register
City of Pinehurst. citation].
----------------------------------------------------------------------------------------------------------------
PART 81--DESIGNATION OF AREAS FOR AIR QUALITY PLANNING PURPOSES
0
3. The authority citation for part 81 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
0
4. In Sec. 81.313, the table entitled ``Idaho-PM-10'' is amended by
revising the entry for ``Eastern Washington-Northern Idaho Interstate
AQCR 62 (Idaho portion):'' to read as follows:
Sec. 81.313 Idaho.
* * * * *
Idaho PM-10
--------------------------------------------------------------------------------------------------------------------------------------------------------
Designation Classification
Designated area -------------------------------------------------------------------------------------------------------------------
Date Type Date Type
--------------------------------------------------------------------------------------------------------------------------------------------------------
* * * * * * *
Eastern Washington-Northern Idaho
Interstate AQCR 62 (Idaho portion):
Shoshone County: Pinehurst October 11, 2018........... Attainment................. ........................... ...........................
Expansion Area Northwest
quarter of the Northwest
quarter, Section 8, Township 48
North, Range 2 East; Southwest
quarter of the Northwest
quarter, Section 8, Township
48, North, Range 2 East;
Northwest quarter of the
Southwest quarter, Section 8,
Township 48 North, Range 2
East; Southwest quarter,
Section 8, Township 48 North,
Range 2 East; Southwest quarter
of the Southwest quarter,
Section 48 North, Range 2 East,
Boise Base (known as
``Pinehurst expansion area'').
City of Pinehurst............... October 11, 2018........... Attainment................. ........................... ...........................
* * * * * * *
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* * * * *
[FR Doc. 2018-19600 Filed 9-10-18; 8:45 am]
BILLING CODE 6560-50-P