Air Plan Approval; AK, Fairbanks North Star Borough; 2006 24-Hour PM2.5, 52997-53004 [2021-20396]
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Federal Register / Vol. 86, No. 183 / Friday, September 24, 2021 / Rules and Regulations
II. Public Comments and EPA Responses
III. Final Action
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R10–OAR–2021–0060; FRL–8909–02–
R10]
Air Plan Approval; AK, Fairbanks North
Star Borough; 2006 24-Hour PM2.5
NAAQS Serious Area Plan
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is approving parts of state
implementation plan (SIP) submissions,
submitted by the State of Alaska (Alaska
or the State) to address Clean Air Act
(CAA or Act) requirements for the 2006
24-hour fine particulate matter (PM2.5)
national ambient air quality standards
(NAAQS) in the Fairbanks North Star
Borough PM2.5 nonattainment area
(Fairbanks PM2.5 Nonattainment Area).
The EPA is also approving rule
revisions and an associated air quality
control plan chapter submitted by
Alaska into the federally-approved SIP.
Alaska made these submissions on
October 25, 2018, November 28, 2018,
December 13, 2019, (Fairbanks Serious
Plan) and December 15, 2020.
DATES: This action is effective on
October 25, 2021.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–R10–OAR–2021–0060. 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 (CBI) or other information
whose disclosure 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:
Matthew Jentgen, EPA Region 10, 1200
Sixth Avenue—Suite 155, Seattle, WA,
98101, (206) 553–0340,
jentgen.matthew@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document wherever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, it is
intended to refer to EPA.
SUMMARY:
Table of Contents
I. Background
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I. Background
On February 22, 2021, the EPA
published its proposal to approve parts
of the Fairbanks Serious Plan and
associated SIP revisions (86 FR 10511).
Specifically, we proposed to approve
the submitted revisions to the Alaska
SIP as meeting the base year emissions
inventory and precursor demonstration
requirements triggered for the Fairbanks
PM2.5 Nonattainment Area upon
reclassification of the area to Serious on
May 10, 2017 (82 FR 21711). The EPA
also proposed to approve as SIPstrengthening the submitted sections of
the Alaska Air Quality Control Plan for
the Fairbanks PM2.5 Nonattainment
Area, state effective January 8, 2020,
related to the Emergency Episode Plan.
The EPA also proposed to approve and
incorporate by reference as SIPstrengthening the submitted regulatory
changes to Alaska Administrative Code
Title 18, Environmental Conservation,
Chapter 50, Air Quality Control (18
AAC 50). The reasons for our proposed
approval are described in the EPA’s
February 22, 2021, proposal and will
not be restated here (86 FR 10511).
II. Public Comments and EPA
Responses
The EPA provided a 30-day period for
the public to comment on the proposed
action that ended on March 24, 2021.
We received 19 public comments. The
public comments can be found in the
docket for this action. Each of the 19
comments raise concerns about a suite
of measures Alaska included under 18
AAC 50.077 that prohibit the
installation, reinstallation, sale, lease,
distribution, or conveyance of woodfired heating devices in the Fairbanks
PM2.5 Nonattainment Area.
Comment 1: The Hearth, Patio &
Barbecue Association (HPBA), Blaze
King Industries, Inc., Hearth & Home
Technologies, Inc., Jotul, Kozy Heat
Fireplaces, Kuma Stoves, Inc.,
Woodstock Soapstone Company, Myren
Consulting, Inc., Rais, Fireplace
Products International Ltd. (FPI), Travis
Industries, United States Stove
Company, and two anonymous
commenters raise concerns about the
State’s submitted revisions to heating
device requirements established in
regulation at 18 AAC 50.077. The
current SIP-approved heating device
requirements in this rule place
restrictions on wood-fired hydronic
heaters and wood-fired heating devices
with a manufacturer-rated heat output
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capacity of less than 350,000 British
Thermal Units (BTUs) per hour and
prohibit the installation, reinstallation,
sale, lease, distribution, or conveyance
of a woodstove in the area, unless:
• The EPA has certified the device
under 40 CFR 60.533; and
• an EPA-accredited lab has tested
the woodstove and determined it meets
an emissions limit of 2.5 grams per
hour, and
Æ the test results were obtained using
EPA New Source Performance Standard
(NSPS) for new residential wood heaters
test procedures (40 CFR part 60,
appendix A, Methods 28, 28A, and
28R), or alternative cordwood methods
that have been approved by the EPA,
and
• the test results were obtained using
EPA NSPS emissions concentration
measurement procedures (40 CFR part
60, appendix A, Methods 5G and 5H).
The submitted SIP revisions tighten
the applicable woodstove emissions
limit from 2.5 grams/hour to 2.0 grams/
hour, require that alternative methods
used to test a woodstove be approved by
both the EPA and the Alaska
Department of Environmental
Conservation (ADEC), and specify that
during testing, a woodstove must not
emit more than 4 grams/hour or 6
grams/hour depending on the test
methods and measurement procedures
used. Specifically, the submissions
revise the regulation at 18 AAC 50.077
to prohibit the installation,
reinstallation, sale, lease, distribution,
or conveyance of a woodstove in the
area, unless: 1
• The EPA has certified the device
under 40 CFR 60.533, and
• an EPA-accredited lab has tested
the woodstove and determined it meets
an emission limit of 2.0 grams per hour,
and
Æ the test results were obtained using
EPA NSPS test procedures (Methods 28,
28A, or 28R), or alternative test
methods, including broadly applicable
test methods, if approved by both EPA
and the Alaska Department of
Environmental Conservation; and
Æ the test results were obtained using
EPA NSPS emission concentration
measurement procedures (Methods 5G
and 5H); and
Æ After September 1, 2020, the test
results must demonstrate: (1) No rolling
1 Other components of 18 AAC 50.077 were
largely retained, such as the requirements for
woodstoves and pellet stoves under 18 AAC
50.077(c) applying to devices with a manufacturerrated heat output capacity of less than 350,000 Btu
per hour, and that the EPA certification should be
calculated in grams per hour and approved by the
department with supporting data.
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60-minute period exceeds 4 grams per
hour using a tapered element oscillating
microbalance (TEOM) following
procedures set out in the Northeast
States for Coordinated Air Use
Management (NESCAUM) Standard
Operating Procedures; or (2) no reported
valid test run measurement (one-hour
filter data) exceeds 6 grams per hour
from the EPA certification report for the
device. See 18 AAC 50.077(c)(b)(ii).
The commenters assert that the new
test requirements at 18 AAC
50.077(c)(b)(ii) are not reliable
indicators of device performance, and
that there is insufficient information to
approve the use of these test
requirements. One commenter, Jotul,
states that the one-hour emissions limit
established by ADEC is completely
arbitrary, and Jotul considers it of
utmost importance that any new
regulations be developed and
promulgated based on sound scientific
principles combined with robust data to
support the conclusions for establishing
new emissions limits and testing
protocol.
Hearth & Home Technologies, Inc.,
Jotul, Kozy Heat Fireplaces, Woodstock
Soapstone Company, Myren Consulting,
Inc., FPI, Travis Industries, and United
States Stove Company do not support
relying on the TEOM method.
According to these commenters, TEOM
is a new test that has not undergone
significant testing and research and
relies on NESCAUM guidance
documents that have not undergone
peer review.
Blaze King Industries, Inc. and
Woodstone Soapstone Company also
note the difficulty working with the
TEOM device, which might jeopardize
the potential for a qualified sample
catch and invalidate an otherwise valid
test run. Woodstone Soapstone
Company notes that there is no
definitive method that correlates results
captured from a TEOM to results from
Method 28 (EPA-approved woodstove
device test method). Kozy Heat
Fireplaces states that the TEOM
equipment has not been tested or
incorporated into the Federal
certification process and has shown
significant variances in testing. An
anonymous commenter notes that
different stoves burn differently and the
total amount of emissions over a burn
cycle should be the relevant metric,
rather than a one-hour measurement.
Myren Consulting states that the 6
grams per hour limit is arbitrary and
capricious because it does not
differentiate between the two applicable
test methods, EPA M28/28R and
American Society for Testing and
Materials (ASTM) E3053, which have
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drastically different operating and
fueling protocols. Myren Consulting
also notes that the 6 gram per hour limit
is being applied in an ex post facto
manner and that, had manufacturers
known about this limit in advance, they
would have had the opportunity to
change their woodstove designs and
bring their stoves into compliance.
Further, HPBA, Innovative Hearth
Products (IHP), Kozy Heat Fireplaces,
Woodstock Soapstone Company, Myren
Consulting, Inc., New Buck Corporation,
Rais, FPI, Travis Industries, United
States Stove Company, and four
anonymous commenters assert that the
additional device requirements for new
woodstoves and pellet stoves, included
in 18 AAC 50.077(c)(b)(ii), are
inconsistent with the Federal NSPS
requirements and that the hourly
measurements depart from the weighted
average emissions limit methodology
relied on by the EPA’s NSPS. IHP states
that individual test runs are conducted
as part of a calculation that establishes
an overall weighted emissions average
that is then compared to standards that
have been developed as per ASTM
methods. The commenters state that
individual test runs cannot in and of
themselves establish a weighted average
and therefore cannot determine the
overall usage expectancy of any multirate appliance and that any such
conjectures by the State of Alaska are
erroneous and without merit.
Blaze King Industries, Inc. asserts that
the one-hour filter pull requirement for
all test runs has eliminated one of the
cleanest burning woodstoves (30.2
series by Blaze King), based on an EPA
weighted average. Blaze King Industries,
Inc. provides data to support the
contention that, during one woodstove
device test, the wood did not collapse
uniformly, with one piece shifting
slightly forward, which resulted in a
one-hour filter pull of 8 grams per hour.
Blaze King Industries, Inc. states other
stoves that are approved for sale in the
Fairbanks PM2.5 Nonattainment Area
have weighted emissions averages more
than twice that of the particular Blaze
King device. Woodstock Soapstone
Company and Rais also provide an
example each of a woodstove that has
one of the lowest weighted average
emissions of all EPA-certified
woodstoves, but due to one test run
exceeding 6 grams per hour, would not
be approved for sale in the Fairbanks
PM2.5 Nonattainment Area.
Another anonymous commenter states
that non-catalytic stoves are more userfriendly and require less maintenance,
but they are more likely to be rejected
under this one-hour requirement
because non-catalytic stoves require
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more heat to burn cleanly, and they take
time to heat up and start burning
cleanly. Hearth & Home Technologies,
Inc. asserts that the clearest path to
cleaner air in the Fairbanks PM2.5
Nonattainment Area is by removing
older, pre-1988 wood-burning devices,
not by prohibiting certain EPA-certified
devices that do not meet Alaska’s
revised requirements in 18 AAC 50.077.
Response 1: For the ensuing reasons,
the comments do not demonstrate that
approval of Alaska’s revisions to 18
AAC 50.077 is inconsistent with the
CAA; therefore, the EPA is finalizing its
approval as proposed. Regarding
Alaska’s rule revisions for wood-fired
heating device emission standards
under 18 AAC 50.077, the EPA
proposed to find that the revisions
submitted by ADEC are more stringent
than the current EPA-approved rules.
For the reasons stated in our proposal
and in this response, we find that
Alaska was not unreasonable in
requiring additional testing
requirements as a method of regulating
the installation and operation of
woodstoves. As stated in a prior EPA
action on November 27, 2018 (83 FR
60769), approving the Alaska SIP as
meeting specific infrastructure
requirements for the 1997, 2006, and
2012 PM2.5 NAAQS, the EPA disagrees
with the premise that states cannot
regulate a source category more
stringently than may be required in a
Federal regulation. The EPA’s role is to
review and approve state choices if they
meet the CAA requirements. There is
nothing in the CAA that prevents SIP
provisions from being more stringent
than Federal NSPS standards. To the
contrary, CAA section 116 explicitly
authorizes states to regulate sources
more stringently than the EPA does
through Federal regulations. Thus, the
fact that 18 AAC 50.077 is more
stringent than the NSPS for new
residential wood heaters does not
impact the approvability of these
control measures as SIP-strengthening.
In addition, ADEC addressed similar
comments during the State’s public
comment period on the SIP revisions. In
the Alaska Department of
Environmental Conservation’s Response
to Comments on the proposed
regulations (ADEC Response to
Comments),2 ADEC asserted that the
purpose of these additional testing
requirements is to better reflect actual
emissions of wood heaters in the
Fairbanks PM2.5 Nonattainment Area.
2 Alaska Department of Environmental
Conservation, Response to Comments on May 14,
2019, Proposed Regulations, November 19, 2019.
Pages 37–38, 51–53.
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ADEC asserted that the current test
method for woodstoves that results in
the certification value (grams of PM2.5
per hour) averages emissions over four
steady-state runs. The values from each
of these runs is an average emission rate
over the time it takes to burn 100% of
the full load of wood used for each run.
This approach translates into a
certification value that is an average of
an average. ADEC stated that averaging
results multiple times minimizes
emission rates, which results in
certification values that may vastly
under predict actual in-use emission
rates and does not reflect the fuel
loading events that in field use may
occur multiple times per day. Further,
ADEC stated that real-time PM2.5
measurements collected from EPA
certification tests have shown that the
maximum emission rate occurs within
two hours of the test period, and
typically, on average, appliances spend
approximately 50% of the certification
testing time in the period known as the
charcoal tail, where virtually no
emissions occur, and in some cases
filters may experience particulate loss
due to warm dry air blowing through
the filter. While this test method
approach differs from the NSPS for new
residential wood heaters, EPA finds
ADEC’s rationale for the revisions to 18
AAC 50.077 is reasonable and a rational
attempt to strengthen rules for the
residential space heating source
category.
With respect to the inclusion of the
TEOM measurement requirement, ADEC
states that the goal was to achieve a 1.0
grams per hour emission limit in
practice, taking into consideration the
variability of emissions when burning
cordwood. After reviewing public
comments submitted during the State’s
public comment period, ADEC amended
the final regulation to provide an
alternative to the TEOM test method
while still providing what it considered
to be an equivalent, if not better, air
quality result than a 1.0 grams per hour
average emission limit. The final
regulation stipulates that manufacturers
may provide the TEOM data as ADEC
originally proposed, with the additional
specificity that no rolling 60-minute
period may exceed 4.0 grams per hour,
or alternatively, by utilizing existing
EPA certification test data showing that
no valid one-hour filter measurement
from the certifying report to EPA is
greater than 6.0 grams per hour.
ADEC asserted that, while this limit is
three times the final ADEC standard
(certification value of 2.0 grams per
hour or less), the limit will apply to all
woodstoves being installed, reinstalled,
sold, leased, distributed, or conveyed in
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the nonattainment area (not just noncatalytic devices). Due to a number of
devices expected to exceed this limit
based on the revised test method, the
result will be fewer devices available for
installation, sale, lease, distribution, or
conveyance in the area. ADEC noted
this approach is designed to ensure that
performance of the devices under more
real-world operations will be more
consistent because the emissions limit
value is not an average. As an example,
ADEC found devices that meet the 1.0
grams per hour emissions limit (adopted
in Missoula County, Montana), but that
exceed the one-hour filter measurement
of 6.0 grams per hour.
Further, ADEC noted that, while the
TEOM is a new approach for wood
heater device certification testing, it has
been incorporated into a standard test
method (ASTM D6831–11) for stack gas
testing. ADEC believes the TEOM test is
a valuable tool that should be used in
future device certification test
requirements and has maintained it as
one option for meeting testing
requirements in the final regulation.
ADEC stated that it is specifying use of
the TEOM and its alternative one-hour
filter measurement is based on the
ADEC’s analysis of over 60 EPA
approved certification reports, the vast
majority of the tests reviewed were for
EPA Step 2 certification.
Thus, Alaska developed and
implemented additional requirements
for wood-fired heating devices, a 2.0
grams per hour limit for all wood-fired
devices and hourly requirements
measured by a TEOM device or during
the EPA certification process, with the
intention to reduce the emissions from
the home heating source category, the
source category with the highest PM2.5
emissions in the Fairbanks PM2.5
Nonattainment Area. EPA has
determined that Alaska’s revisions to 18
AAC 50.077 are reasonable and
strengthen the SIP with respect to the
regulation of emissions from the
residential space heating source
category.
Comment 2: HPBA, Kozy Heat
Fireplaces, and Travis Industries assert
that the one-hour filter alternative is not
compatible with woodstove emissions
and the Federal air quality standard that
the EPA based on data averaged over 24
hours, noting that the Federal air quality
standard is not a ‘‘peaking’’ standard
that is violated by a single episodic,
one-hour reading. Thus, the commenters
assert that the EPA was proposing to
approve this metric without any
explanation in the record of its
relevance to the nonattainment issues
experienced in the Fairbanks PM2.5
Nonattainment Area.
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Response 2: The EPA disagrees with
the commenters. First, the EPA
disagrees with the commenters’
assertion that device requirements must
be directly tied to the Federal air quality
standard. Overall, the EPA notes that
PM2.5 is a complex and highly variable
mixture of particles and gases. The
EPA’s PM2.5 Implementation Rule (81
FR 58010, August 24, 2016)
recommends that states should base
potential control measures in part on an
analysis of emissions inventory data
summaries, fine particle speciation
monitoring data, and source
apportionment air quality modeling
data. Emissions standards can have
different averaging periods based on the
type of source, rate of emissions, and
control measure. Irrespective of the
particular NAAQS, our basis for
approval here is that Alaska’s revisions
to 18 AAC 50.077 render the SIP more
stringent than the prior approved rule in
terms of regulating emissions from
woodstoves. The EPA finds that ADEC’s
rationale for why the revised 18 AAC
50.077 will reduce emissions from the
residential home heating source
category is reasonable.
Second, the record contains ample
information showing that ADEC’s
revised rule will reduce emissions of
direct PM2.5 from the residential home
heating source category. The EPA
evaluated ADEC’s SIP submission,
including the responses to similar
comments in the development of the
State’s regulation. In ADEC’s Response
to Comments, ADEC noted that, under
the 2015 NSPS for new residential wood
heaters, the EPA required reporting of
emission rates for the first hour of the
test period. This data reflects the timing
and emission rates typically associated
with the 60-minute test requirements for
particulate matter testing at all other
sources (EPA Method 5). ADEC asserted
that the assessment of one-hour data
allows agencies to gauge performance
and determine which appliances are
low emitting from the start of the
certification test versus those that have
been able to design for long charcoal
tails to minimize the peak emissions.
ADEC additionally stated that one of the
reasons for requiring the use of TEOM
measurement data is to provide a more
meaningful equivalency to a 1.0 grams
per hour average emission limit (as
adopted by Missoula County, Montana),
taking into consideration the variability
of emissions when burning cordwood,
while still allowing a range of devices
to be sold and used in the Fairbanks
PM2.5 Nonattainment Area. Thus, the
record does contain information
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explaining the reason for the one-hour
filter alternative.
Finally, as stated in a prior EPA
action on November 27, 2018 (83 FR
60769), approving the Alaska SIP as
meeting specific PM2.5 infrastructure
requirements, states have the obligation
to regulate sources as necessary to meet
nonattainment area plan stringency
requirements, such as reasonably and
best available control measures, and the
obligation to regulate sources as
necessary to attain the NAAQS in a
given nonattainment area. ADEC
determined it was necessary to revise 18
AAC 50.077 and submitted the revisions
to address Serious area planning
requirements for best available control
measures in the Fairbanks PM2.5
Nonattainment Area. While this action
does not address whether the submitted
revisions to 18 AAC 50.077 and other
rules are sufficient to meet best
available control measure requirements,
we explained in our proposed action
how the revisions strengthen the SIP.
The comments do not demonstrate that
Alaska’s revisions to 18 AAC 50.077 or
rationale for these revisions are
unreasonable, and EPA is thus finalizing
approval of 18 AAC 50.077 as proposed.
Comment 3: HPBA, Blaze King
Industries, Inc., Hearth & Home
Technologies, Inc., Travis Industries,
and United States Stove Company note
that Fairbanks has a unique winter
environment where woodstoves are only
‘‘started’’ once during winter and left
running during entire cold season.
Thus, the commenters assert that
establishing a particulate emissions
standard based only on the first hour of
operation inaccurately represents the
emissions of wood-fired heating devices
in the Fairbanks PM2.5 Nonattainment
Area. In addition, Blaze King Industries,
Inc. states that woodstove users in the
Fairbanks North Star Borough are
unique in their use of stoves to address
sub-zero climate conditions in the
region. Myren Consulting states that, no
matter the test method, testing of
certified stoves in the test environment
will not reflect conditions in the field
because of differences in static pressure,
that the commenter asserts will
significantly affect performance in areas
with colder temperatures such as in
Fairbanks.
Response 3: As noted in Responses 1
and 2, ADEC revised 18 AAC 50.077 to
reduce emissions from wood-fired
heating devices while allowing for sale
and use of a range of devices in the
Fairbanks PM2.5 Nonattainment Area. In
ADEC’s Response to Comments, ADEC
stated that the TEOM measurement and
the one-hour filter pull data reflect more
real-time particulate matter
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measurements and that other test
methods, based on an average of
multiple test runs, may vastly under
predict actual in-use emission rates and
do not reflect the actual fuel loading
events that may occur multiple times
per day. Moreover, ADEC developed
this control measure as part of its
control measure analysis that
incorporates the emissions inventory,
speciation, and source apportionment
data for the nonattainment area. Based
on ADEC’s SIP submission, including
the responses to comments in ADEC’s
rulemaking process, the EPA finds that
ADEC’s rationale for incorporating the
TEOM measurement and the one-hour
filter pull data is credible and based on
a robust understanding of the emissions
from woodstoves. Therefore, the EPA is
approving this rule revision as SIPstrengthening because the revised rule
imposes requirements for woodstoves in
the Fairbanks PM2.5 Nonattainment Area
that are more stringent than the
woodstove requirements in the current
SIP.
Comment 4: Travis Industries asserts
that the EPA must expressly state that
the standards ADEC is imposing in 18
AAC 50.077 are inappropriate in other
settings that do not share the Fairbanks
PM2.5 Nonattainment Area’s extreme
climatic conditions.
Response 4: As specified in 18 AAC
50.077, this regulation only applies to
qualifying wood-fired heating devices in
areas in Alaska that are designated
nonattainment for PM2.5, under 18 AAC
50.015(b)(3). Currently the Fairbanks
and North Pole urban area (i.e.,
Fairbanks PM2.5 Nonattainment Area) is
listed as the only nonattainment area in
Alaska where this regulation applies.
However, other state and local
governments have the authority to adopt
similar measures.
Comment 5: Comments by HPBA,
Blaze King Industries, Inc., Kuma
Stoves, Inc., IHP, Woodstock Soapstone
Company, Myren Consulting, and FPI
object to Alaska’s authority to validate
the EPA’s wood-fired heating device
certifications for applicability in the
Fairbanks PM2.5 Nonattainment Area
and limit the EPA-approved applicable
testing methods. HPBA asserts that,
under 18 AAC 50.077(c)(3)(A), ADEC
can effectively veto an EPA device
certification on the grounds that ADEC
had not approved the same alternative
test method. As an example, HPBA
notes that while the EPA approved
ASTM 3053 (cordwood test method),
Alaska has not. These commenters state
that Alaska’s failure to recognize this
approved test method undermines the
EPA’s authority. In addition, Kuma
Stoves, Inc. states that the EPA should
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not now, after benefitting from valuable
data generated by the ASTM 3053 test
method, support language that declares
ASTM 3053 to be a nonrepresentative
test. One anonymous commenter
contends that, based on experience as a
manufacturer of EPA-certified
woodstoves, the ASTM 3053 test
method is credible and produces
consistent and reliable emissions
values, and therefore rejecting this test
method results in less informative
testing data.
Generally, IHP states that it is onerous
for a state to regulate an industry to
meet any requirements that are not
previously set and known before
development, certification, and
manufacturing of those industry
products. Kozy Heat Fireplaces, Inc.
states these device requirements impose
new and greater costs for certification
and that these costs have not been
quantified by either ADEC or the EPA.
IHP recommends that the EPA reject
ADEC’s revised requirements for
woodstoves in the Alaska SIP
submission as a ‘‘de facto federal
standard,’’ and in the comment
encourages the State of Alaska to work
with the industry to find a more
complete solution. FPI also notes that,
not only does ADEC not recognize the
alternate test method, but it does not
recognize the 2.5 grams per hour
emissions limit associated with this test
method. FPI asserts that dismissing this
limit by setting a 2.0 grams per hour
limit for cordwood without a scientific
process and peer review is arbitrary.
An anonymous commenter notes that
the same entities are involved in
woodstove device testing certifications
and accreditations as product safety
testing. The commenter states that
laboratories need an International
Organization for Standardization (ISO)
17025 accreditation that can be renewed
every two years following an official
audit from the accreditor. The
commenter states that proficiency
testing has been put in place by the EPA
as part of the ISO–17025 accreditation
and all accredited laboratories should
comply with the proficiency testing
every two years.
Response 5: The EPA disagrees with
the commenters’ assertion that Alaska
lacks authority to promulgate rules that
are more stringent than EPA’s NSPS or
that otherwise limit the range of devices
allowed in the area. The EPA also
disagrees with the assertion that Alaska,
by promulgating these rules, establishes
a ‘‘de facto federal standard’’ and as
such undermines the EPA’s
independent authorities to establish
Federal new source performance
standards. Congress gave the EPA
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53001
under 18 AAC 50.077(a) that prohibits
the sale and installation of cordwoodfueled outdoor hydronic heaters in the
Fairbanks PM2.5 Nonattainment Area.
Central Boiler/Woodmaster states that
these devices are not given
consideration by the state based on
emissions or performance like other
wood heating appliances.
Response 6: Consistent with CAA
requirements and the EPA’s PM2.5
Implementation Rule, Alaska has
authority to prohibit the sale and
installation of devices that contribute to
PM2.5 concentrations in the Fairbanks
PM2.5 Nonattainment Area, such as
cordwood-fueled outdoor hydronic
heaters, to bring the area into
attainment. We note that, under 18 AAC
50.077(b), Alaska does permit pelletfueled wood-fired hydronic heaters for
use in the Fairbanks PM2.5
Nonattainment Area, if specific device
performance criteria meet Alaska
regulations. Therefore, the EPA is
finalizing the approval of 18 AAC
50.077(b) as proposed.
Comment 7: HPBA notes that while
point sources (electric power plants)
constitute the largest source of SO2
emissions in the Fairbanks PM2.5
Nonattainment Area, ADEC, in many
instances, did not require additional
source-level controls on several large
facilities. HPBA states that ADEC did
not require installation of new control
technologies for SO2 even though the
average daily emissions from these
point sources are nearly three times
larger than sources of directly-emitted
PM2.5 from woodstoves.
Response 7: The EPA agrees with the
commenter that the largest source
category of SO2 emissions is point
sources, including electric power plants,
and that SO2 is a significant contributor
to PM2.5 concentrations in the Fairbanks
PM2.5 Nonattainment Area. On
December 13, 2019, Alaska submitted a
best available control technology
(BACT) control analysis for specific
point sources located in the area,
including several electric power plants,
as part of the Fairbanks Serious Plan.
However, we consider this comment to
be outside the scope of this action. In
this action, the EPA is evaluating rule
revisions that ADEC has adopted to
address direct PM2.5 emissions from
wood-fired heating devices. We did not
propose action on the BACT Serious
area planning requirements, including
the issue of appropriate regulation of
SO2 emissions from point sources, as
part of this action. We intend to address
Alaska’s best available control measures
(BACM)/BACT control analysis, and any
supplemental BACT control analysis
submissions, in a separate action. We
Continued
authority in CAA section 111 to
establish performance standards for
categories of new sources. Distinct from
CAA section 111, Congress required in
CAA section 110 that states have an
overarching SIP to implement, maintain,
and enforce the NAAQS. If states have
designated nonattainment areas, then
they must make a nonattainment plan
SIP submission meeting additional
specific requirements. State regulation
of sources more stringently for purposes
of meeting SIP requirements does not
interfere or undermine the EPA’s
authority to regulate new sources under
the CAA. With few exceptions, states
are not preempted from regulating
source categories more stringently and
have explicit authority in CAA section
116 to do so.
The EPA disagrees with the
commenters’ assertion that ADEC did
not consider compliance costs. In
ADEC’s Response to Comments, Alaska
acknowledged the potential increased
costs to certification testing. ADEC
stated that the intention is to provide a
meaningful equivalent control measure
to a 1.0 grams per hour average
emissions limit, while also allowing a
range of devices to be sold and used in
the Fairbanks PM2.5 Nonattainment
Area. As discussed in Response 1 in this
preamble, states have explicit authority
to regulate a source category more
stringently than may be required in a
Federal regulation. The EPA’s role is to
review and approve state choices if they
meet applicable CAA requirements. See
42 U.S.C. 7410(k) and 40 CFR 52.02(a);
see also Union Elec. Co. v. EPA, 427
U.S. 246, 256–266 (1976) (holding that
the EPA may not disapprove a state
implementation plan that meets the
requirements of CAA Section 110(a)(2)
on the basis of technological or
economic infeasibility). There is nothing
in the CAA that prevents states from
imposing SIP requirements that are
more stringent than Federal NSPS
standards.
Regarding woodstove device testing
certifications and ISO–17025
accreditations, the 2015 NSPS stipulates
that for new residential wood heaters,
new residential hydronic heaters, and
forced-air furnaces (80 FR 13672), a test
laboratory must agree to participate
biennially in an independently operated
proficiency testing program with no
direct ties to the participating
laboratories. Further, the EPA
Administrator may revoke a test
laboratory approval if a test laboratory
has failed to participate in a proficiency
testing program, in accordance with 40
CFR 60.535.
Comment 6: Central Boiler/
Woodmaster objects to the provision
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encourage the commenter to resubmit
the comment during the public
comment period of our future action on
the BACT control analysis.
Conclusion
The EPA finds that the comments do
not change our proposed determination
that the regulations submitted by Alaska
are consistent with CAA requirements
and strengthen the SIP. Therefore, we
are finalizing our action as proposed.
III. Final Action
In this action, the EPA is approving a
portion of the submitted revisions to the
Alaska SIP as meeting the following
Serious Plan required elements for the
Fairbanks PM2.5 Nonattainment Area:
• The 2013 base year emissions
inventory (CAA section 172(c)(3); 40
CFR 51.1008(b)(1)); and
• The State’s PM2.5 precursor
demonstration for NOX and volatile
organic compound (VOC) emissions
(CAA section 189(e); 40 CFR
51.1006(a)).
We reiterate that Alaska’s precursor
analysis did not address nonattainment
New Source Review (NSR)
requirements. The State made the prior
determination to regulate all four EPA
identified legal precursors to PM2.5 in
the nonattainment NSR regulations
applicable to the Fairbanks PM2.5
Nonattainment Area. The EPA approved
Alaska’s October 25, 2018, SIP revision
as meeting the nonattainment NSR
requirements triggered upon
reclassification of the area to Serious
(August 29, 2019, 84 FR 45419).
Specifically, the EPA is approving the
submitted sections of the Alaska Air
Quality Control Plan for the Fairbanks
PM2.5 Nonattainment Area, State
effective January 8, 2020:
• Volume II Section III.D.7.06 and
Volume III Section III.D.7.06 Emissions
Inventory, for purposes of the 2013 base
year emissions inventory;
• Volume II Section III.D.7.08
Precursor Demonstration, for the
purposes of NOX and VOC emissions as
it relates to BACM/BACT control
measure requirements; and
Further, the EPA is approving the
submitted section of the Alaska Air
Quality Control Plan for the Fairbanks
PM2.5 Nonattainment Area, State
effective December 25, 2020:
• Volume II Section III.D.7.12,
Emergency Episode Plan.3
3 Submitted on December 15, 2020 and included
in the docket. The EPA is not at this time
determining whether this updated planning
chapter, in conjunction with the associated
regulatory changes, meets other Serious area
nonattainment plan requirements for the 2006 24-
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In addition, the EPA is approving and
incorporating by reference the
submitted regulatory changes listed
below into the Alaska SIP. As stated in
our proposal, the EPA is not at this time
determining whether these provisions
also meet other Serious area
nonattainment plan requirements for the
Fairbanks PM2.5 Nonattainment Area.
Upon the effective date of this action,
the Alaska SIP will include:
• 18 AAC 50.030, except (a), State
effective January 12, 2018;
• 18 AAC 50.075, except (d)(2) and
(f), State effective January 8, 2020;
• 18 AAC 50.076, except (g)(11), State
effective January 8, 2020;
• 18 AAC 50.077, except (g) and (q),
State effective January 8, 2020;
• 18 AAC 50.078, except (c) and (d),
State effective January 8, 2020;
• 18 AAC 50.079, except (e), State
effective January 8, 2020; and
• 18 AAC 50.990(71), (138), (149),
(150), (151), (152), (153), (154), and
(155), State effective January 8, 2020.
IV. Incorporation by Reference
In this document, the EPA is
finalizing regulatory text in an EPA final
rule that includes incorporation by
reference. In accordance with
requirements of 1 CFR 51.5, the EPA is
finalizing the incorporation by reference
the regulations described in Section III
of this preamble. The EPA has made,
and will continue to make, these
materials generally available through
https://www.regulations.gov and at the
EPA Region 10 Office (please contact
the person identified in the FOR FURTHER
INFORMATION CONTACT section of this
preamble for more information).
Therefore, these materials have been
approved by the EPA for inclusion in
the State implementation plan, have
been incorporated by reference by the
EPA into that plan, are fully federally
enforceable under sections 110 and 113
of the CAA as of the effective date of the
final rulemaking of the EPA’s approval,
and will be incorporated by reference by
the Director of the Federal Register in
the next update to the SIP compilation.
V. Statutory and Executive Order
Reviews
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA 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
hour PM2.5 NAAQS in the Fairbanks PM2.5
Nonattainment Area.
VerDate Sep<11>2014
16:01 Sep 23, 2021
Jkt 253001
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);
• 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 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 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
PO 00000
Frm 00052
Fmt 4700
Sfmt 4700
Congress and to the Comptroller General
of the United States. 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 ‘‘major rule’’ as
defined by 5 U.S.C. 804(2).
Under section 307(b)(1) of the Clean
Air Act, petitions for judicial review of
this action must be filed in the United
States Court of Appeals for the
appropriate circuit by November 23,
2021. 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 in 40 CFR Part 52
Environmental protection, Air
pollution control, Carbon monoxide,
Incorporation by reference,
Intergovernmental relations, Lead,
Nitrogen dioxide, Ozone, Particulate
matter, Reporting and recordkeeping
requirements, Sulfur oxides, Volatile
organic compounds.
Dated: September 15, 2021.
Michelle L. Pirzadeh,
Acting Regional Administrator, Region 10.
For the reasons set forth in the
preamble, 40 CFR part 52 is amended as
follows:
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 C—Alaska
2. In § 52.70:
a. The table in paragraph (c) is
amended by:
■ i. Adding the entry ‘‘18 AAC 50.030’’
in numerical order;
■ ii. Revising the entries ‘‘18 AAC
50.075’’, ‘‘18 AAC 50.076’’, and ‘‘18
AAC 50.077’’;
■ iii. Adding the entries ‘‘18 AAC
50.078’’ and ‘‘18 AAC 50.079’’ in
numerical order; and
■ iv. Revising the entry ‘‘18 AAC
50.990’’.
■
■
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Federal Register / Vol. 86, No. 183 / Friday, September 24, 2021 / Rules and Regulations
b. The table in paragraph (e) is
amended by adding the entries
‘‘II.III.D.7.06 Fairbanks Emissions
Inventory Data’’, ‘‘III.III.D.7.06
Appendix to Fairbanks Emissions
Inventory Data’’, ‘‘II.III.D.7.08 Fairbanks
Modeling’’, and ‘‘II.III.D.7.12 Fairbanks
Emergency Episode Plan’’ to the end of
the table.
The additions and revisions read as
follows:
■
§ 52.70
*
Identification of plan.
*
*
(c) * * *
*
*
EPA-APPROVED ALASKA REGULATIONS AND STATUTES
State citation
State
effective
date
Title/subject
EPA approval date
Explanations
Alaska Administrative Code Title 18 Environmental Conservation, Chapter 50—Air Quality Control (18 AAC 50)
18 AAC 50—Article 1. Ambient Air Quality Management
*
18 AAC 50.030 ......
*
*
State Air Quality Control Plan .......
*
18 AAC 50.075 ......
*
*
Solid Fuel-Fired Heating Device
Visible Emission Standards.
Solid Fuel-Fired Heating Device
Fuel Requirements; Requirements for Wood Sellers.
Standards for Wood-Fired Heating
Devices.
Additional Control Measures for a
Serious PM2.5 Nonattainment
Area.
Provisions for Coal-Fired Heating
Devices.
18 AAC 50.076 ......
18 AAC 50.077 ......
18 AAC 50.078 ......
18 AAC 50.079 ......
*
*
*
18 AAC 50.990 ......
*
*
*
*
Except (a).
*
*
*
9/24/2021, [Insert Federal Register citation].
9/24/2021, [Insert Federal Register citation].
*
Except (d)(2) and (f).
*
9/24/2021, [Insert Federal Register citation].
9/24/2021, [Insert Federal Register citation].
Except (g) and (q).
1/8/2020
1/8/2020
1/8/2020
1/8/2020
9/24/2021, [Insert Federal Register citation].
Except (g)(11).
Except (c) and (d).
Except (e).
*
*
*
18 AAC 50—Article 9. General Provisions
*
*
*
9/24/2021, [Insert Federal Register citation].
1/8/2020
*
*
Definitions .....................................
*
*
1/12/2018
*
1/8/2020
*
*
*
9/24/2021, [Insert Federal Register citation].
*
*
*
*
*
*
*
*
(e) * * *
EPA-APPROVED ALASKA NONREGULATORY PROVISIONS AND QUASI-REGULATORY MEASURES
Name of SIP
provision
*
*
II.III.D.7.06
Fairbanks
Emissions
Inventory
Data.
III.III.D.7.06
Appendix
to Fairbanks
Emissions
Inventory
Data.
II.III.D.7.08
Fairbanks
Modeling.
VerDate Sep<11>2014
State
submittal
date
Applicable geographic or
nonattainment area
*
*
*
Recently—Approved Plans
*
*
Fairbanks North Star Borough .........
12/13/2019
Fairbanks North Star Borough .........
Fairbanks North Star Borough .........
16:01 Sep 23, 2021
Jkt 253001
PO 00000
EPA approval date
Explanations
*
*
*
*
*
9/24/2021, [Insert Federal Register
citation].
*
*
Approved for purposes of the Fairbanks Serious Plan 2013 base
year emissions inventory.
12/13/2019
9/24/2021, [Insert Federal Register
citation].
Approved for purposes of the Fairbanks Serious Plan 2013 base
year emissions inventory.
12/13/2019
9/24/2021, [Insert Federal Register
citation].
Approved for purposes of the Fairbanks Serious Plan PM2.5 precursor demonstration for NOX and
VOC emissions as it relates to
BACM/BACT control measure requirements.
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Federal Register / Vol. 86, No. 183 / Friday, September 24, 2021 / Rules and Regulations
EPA-APPROVED ALASKA NONREGULATORY PROVISIONS AND QUASI-REGULATORY MEASURES—Continued
State
submittal
date
Name of SIP
provision
Applicable geographic or
nonattainment area
II.III.D.7.12
Fairbanks
Emergency
Episode
Plan.
Fairbanks North Star Borough .........
[FR Doc. 2021–20396 Filed 9–23–21; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2020–0009; FRL–8785–01–
OCSPP]
Metalaxyl; Pesticide Tolerances
This regulation establishes
tolerances for residues of metalaxyl in
or on black pepper. American Spice
Trade Association requested these
tolerances under the Federal Food,
Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective
September 24, 2021. Objections and
requests for hearings must be received
on or before November 23, 2021, and
must be filed in accordance with the
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
ADDRESSES: The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2020–0009, is
available at https://www.regulations.gov
or at the Office of Pesticide Programs
Regulatory Public Docket (OPP Docket)
in the Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW, Washington, DC
20460–0001. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the OPP
Docket is (703) 305–5805.
Due to the public health concerns
related to COVID–19, the EPA Docket
Center (EPA/DC) and Reading Room is
closed to visitors with limited
exceptions. The staff continues to
provide remote customer service via
email, phone, and webform. For the
latest status information on EPA/DC
VerDate Sep<11>2014
16:01 Sep 23, 2021
Jkt 253001
services and docket access, visit https://
www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Marietta Echeverria, Registration
Division (7505P), Office of Pesticide
Programs, Environmental Protection
Agency, 1200 Pennsylvania Ave. NW,
Washington, DC 20460–0001; main
telephone number: (703) 305–7090;
email address: RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
A. Does this action apply to me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
provides a guide to help readers
determine whether this document
applies to them. Potentially affected
entities may include:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Government Publishing Office’s eCFR site at https://www.ecfr.gov/cgi-bin/
text-idx?&c=ecfr&tpl=/ecfrbrowse/
Title40/40tab_02.tpl.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a, any person may file an
objection to any aspect of this regulation
and may also request a hearing on those
objections. You must file your objection
or request a hearing on this regulation
in accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2020–0009 in the subject line on
PO 00000
Frm 00054
Explanations
9/24/2021, [Insert Federal Register
citation].
I. General Information
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY:
12/15/2020
EPA approval date
Fmt 4700
Sfmt 4700
the first page of your submission. All
objections and requests for a hearing
must be in writing and must be received
by the Hearing Clerk on or before
November 23, 2021. Addresses for mail
and hand delivery of objections and
hearing requests are provided in 40 CFR
178.25(b), although at this time, EPA
strongly encourages those interested in
submitting objections or a hearing
request, to submit objections and
hearing requests electronically. See
Order Urging Electronic Service and
Filing (April 10, 2020), https://
www.epa.gov/sites/production/files/
2020-05/documents/2020-04-10_-_
order_urging_electronic_service_and_
filing.pdf. At this time, because of the
COVID–19 pandemic, the judges and
staff of the Office of Administrative Law
Judges are working remotely and not
able to accept filings or correspondence
by courier, personal deliver, or
commercial delivery, and the ability to
receive filings or correspondence by
U.S. Mail is similarly limited. When
submitting documents to the U.S. EPA
Office of Administrative Law Judges
(OALJ), a person should utilize the
OALJ e-filing system, at https://
yosemite.epa.gov/OA/EAB/EAB-ALJ_
upload.nsf.
Although EPA’s regulations require
submission via U.S. Mail or hand
deliver, EPA intends to treat
submissions filed via electronic means
as properly filed submissions during
this time that the Agency continues to
maximize telework due to the
pandemic; therefore, EPA believes the
preference for submission via electronic
means will not be prejudicial. If it is
impossible for a person to submit
documents electronically or receive
service electronically, e.g., the person
does not have any access to a computer,
the person shall so advise OALJ by
contacting the Hearing Clerk at (202)
564–6281. If a person is without access
to a computer and must file documents
by U.S. Mail, the person shall notify the
Hearing Clerk every time it files a
document in such a manner. The
address for mailing documents is U.S.
Environmental Protection Agency,
Office of Administrative Law Judges,
E:\FR\FM\24SER1.SGM
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Agencies
[Federal Register Volume 86, Number 183 (Friday, September 24, 2021)]
[Rules and Regulations]
[Pages 52997-53004]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-20396]
[[Page 52997]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R10-OAR-2021-0060; FRL-8909-02-R10]
Air Plan Approval; AK, Fairbanks North Star Borough; 2006 24-Hour
PM2.5 NAAQS Serious Area Plan
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is approving parts
of state implementation plan (SIP) submissions, submitted by the State
of Alaska (Alaska or the State) to address Clean Air Act (CAA or Act)
requirements for the 2006 24-hour fine particulate matter
(PM2.5) national ambient air quality standards (NAAQS) in
the Fairbanks North Star Borough PM2.5 nonattainment area
(Fairbanks PM2.5 Nonattainment Area). The EPA is also
approving rule revisions and an associated air quality control plan
chapter submitted by Alaska into the federally-approved SIP. Alaska
made these submissions on October 25, 2018, November 28, 2018, December
13, 2019, (Fairbanks Serious Plan) and December 15, 2020.
DATES: This action is effective on October 25, 2021.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-R10-OAR-2021-0060. 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 (CBI) or other information whose
disclosure 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: Matthew Jentgen, EPA Region 10, 1200
Sixth Avenue--Suite 155, Seattle, WA, 98101, (206) 553-0340,
[email protected].
SUPPLEMENTARY INFORMATION: Throughout this document wherever ``we,''
``us,'' or ``our'' is used, it is intended to refer to EPA.
Table of Contents
I. Background
II. Public Comments and EPA Responses
III. Final Action
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
I. Background
On February 22, 2021, the EPA published its proposal to approve
parts of the Fairbanks Serious Plan and associated SIP revisions (86 FR
10511). Specifically, we proposed to approve the submitted revisions to
the Alaska SIP as meeting the base year emissions inventory and
precursor demonstration requirements triggered for the Fairbanks
PM2.5 Nonattainment Area upon reclassification of the area
to Serious on May 10, 2017 (82 FR 21711). The EPA also proposed to
approve as SIP-strengthening the submitted sections of the Alaska Air
Quality Control Plan for the Fairbanks PM2.5 Nonattainment
Area, state effective January 8, 2020, related to the Emergency Episode
Plan. The EPA also proposed to approve and incorporate by reference as
SIP-strengthening the submitted regulatory changes to Alaska
Administrative Code Title 18, Environmental Conservation, Chapter 50,
Air Quality Control (18 AAC 50). The reasons for our proposed approval
are described in the EPA's February 22, 2021, proposal and will not be
restated here (86 FR 10511).
II. Public Comments and EPA Responses
The EPA provided a 30-day period for the public to comment on the
proposed action that ended on March 24, 2021. We received 19 public
comments. The public comments can be found in the docket for this
action. Each of the 19 comments raise concerns about a suite of
measures Alaska included under 18 AAC 50.077 that prohibit the
installation, reinstallation, sale, lease, distribution, or conveyance
of wood-fired heating devices in the Fairbanks PM2.5
Nonattainment Area.
Comment 1: The Hearth, Patio & Barbecue Association (HPBA), Blaze
King Industries, Inc., Hearth & Home Technologies, Inc., Jotul, Kozy
Heat Fireplaces, Kuma Stoves, Inc., Woodstock Soapstone Company, Myren
Consulting, Inc., Rais, Fireplace Products International Ltd. (FPI),
Travis Industries, United States Stove Company, and two anonymous
commenters raise concerns about the State's submitted revisions to
heating device requirements established in regulation at 18 AAC 50.077.
The current SIP-approved heating device requirements in this rule place
restrictions on wood-fired hydronic heaters and wood-fired heating
devices with a manufacturer-rated heat output capacity of less than
350,000 British Thermal Units (BTUs) per hour and prohibit the
installation, reinstallation, sale, lease, distribution, or conveyance
of a woodstove in the area, unless:
The EPA has certified the device under 40 CFR 60.533; and
an EPA-accredited lab has tested the woodstove and
determined it meets an emissions limit of 2.5 grams per hour, and
[cir] the test results were obtained using EPA New Source
Performance Standard (NSPS) for new residential wood heaters test
procedures (40 CFR part 60, appendix A, Methods 28, 28A, and 28R), or
alternative cordwood methods that have been approved by the EPA, and
the test results were obtained using EPA NSPS emissions
concentration measurement procedures (40 CFR part 60, appendix A,
Methods 5G and 5H).
The submitted SIP revisions tighten the applicable woodstove
emissions limit from 2.5 grams/hour to 2.0 grams/hour, require that
alternative methods used to test a woodstove be approved by both the
EPA and the Alaska Department of Environmental Conservation (ADEC), and
specify that during testing, a woodstove must not emit more than 4
grams/hour or 6 grams/hour depending on the test methods and
measurement procedures used. Specifically, the submissions revise the
regulation at 18 AAC 50.077 to prohibit the installation,
reinstallation, sale, lease, distribution, or conveyance of a woodstove
in the area, unless: \1\
---------------------------------------------------------------------------
\1\ Other components of 18 AAC 50.077 were largely retained,
such as the requirements for woodstoves and pellet stoves under 18
AAC 50.077(c) applying to devices with a manufacturer-rated heat
output capacity of less than 350,000 Btu per hour, and that the EPA
certification should be calculated in grams per hour and approved by
the department with supporting data.
---------------------------------------------------------------------------
The EPA has certified the device under 40 CFR 60.533, and
an EPA-accredited lab has tested the woodstove and
determined it meets an emission limit of 2.0 grams per hour, and
[cir] the test results were obtained using EPA NSPS test procedures
(Methods 28, 28A, or 28R), or alternative test methods, including
broadly applicable test methods, if approved by both EPA and the Alaska
Department of Environmental Conservation; and
[cir] the test results were obtained using EPA NSPS emission
concentration measurement procedures (Methods 5G and 5H); and
[cir] After September 1, 2020, the test results must demonstrate:
(1) No rolling
[[Page 52998]]
60-minute period exceeds 4 grams per hour using a tapered element
oscillating microbalance (TEOM) following procedures set out in the
Northeast States for Coordinated Air Use Management (NESCAUM) Standard
Operating Procedures; or (2) no reported valid test run measurement
(one-hour filter data) exceeds 6 grams per hour from the EPA
certification report for the device. See 18 AAC 50.077(c)(b)(ii).
The commenters assert that the new test requirements at 18 AAC
50.077(c)(b)(ii) are not reliable indicators of device performance, and
that there is insufficient information to approve the use of these test
requirements. One commenter, Jotul, states that the one-hour emissions
limit established by ADEC is completely arbitrary, and Jotul considers
it of utmost importance that any new regulations be developed and
promulgated based on sound scientific principles combined with robust
data to support the conclusions for establishing new emissions limits
and testing protocol.
Hearth & Home Technologies, Inc., Jotul, Kozy Heat Fireplaces,
Woodstock Soapstone Company, Myren Consulting, Inc., FPI, Travis
Industries, and United States Stove Company do not support relying on
the TEOM method. According to these commenters, TEOM is a new test that
has not undergone significant testing and research and relies on
NESCAUM guidance documents that have not undergone peer review.
Blaze King Industries, Inc. and Woodstone Soapstone Company also
note the difficulty working with the TEOM device, which might
jeopardize the potential for a qualified sample catch and invalidate an
otherwise valid test run. Woodstone Soapstone Company notes that there
is no definitive method that correlates results captured from a TEOM to
results from Method 28 (EPA-approved woodstove device test method).
Kozy Heat Fireplaces states that the TEOM equipment has not been tested
or incorporated into the Federal certification process and has shown
significant variances in testing. An anonymous commenter notes that
different stoves burn differently and the total amount of emissions
over a burn cycle should be the relevant metric, rather than a one-hour
measurement. Myren Consulting states that the 6 grams per hour limit is
arbitrary and capricious because it does not differentiate between the
two applicable test methods, EPA M28/28R and American Society for
Testing and Materials (ASTM) E3053, which have drastically different
operating and fueling protocols. Myren Consulting also notes that the 6
gram per hour limit is being applied in an ex post facto manner and
that, had manufacturers known about this limit in advance, they would
have had the opportunity to change their woodstove designs and bring
their stoves into compliance.
Further, HPBA, Innovative Hearth Products (IHP), Kozy Heat
Fireplaces, Woodstock Soapstone Company, Myren Consulting, Inc., New
Buck Corporation, Rais, FPI, Travis Industries, United States Stove
Company, and four anonymous commenters assert that the additional
device requirements for new woodstoves and pellet stoves, included in
18 AAC 50.077(c)(b)(ii), are inconsistent with the Federal NSPS
requirements and that the hourly measurements depart from the weighted
average emissions limit methodology relied on by the EPA's NSPS. IHP
states that individual test runs are conducted as part of a calculation
that establishes an overall weighted emissions average that is then
compared to standards that have been developed as per ASTM methods. The
commenters state that individual test runs cannot in and of themselves
establish a weighted average and therefore cannot determine the overall
usage expectancy of any multi-rate appliance and that any such
conjectures by the State of Alaska are erroneous and without merit.
Blaze King Industries, Inc. asserts that the one-hour filter pull
requirement for all test runs has eliminated one of the cleanest
burning woodstoves (30.2 series by Blaze King), based on an EPA
weighted average. Blaze King Industries, Inc. provides data to support
the contention that, during one woodstove device test, the wood did not
collapse uniformly, with one piece shifting slightly forward, which
resulted in a one-hour filter pull of 8 grams per hour. Blaze King
Industries, Inc. states other stoves that are approved for sale in the
Fairbanks PM2.5 Nonattainment Area have weighted emissions
averages more than twice that of the particular Blaze King device.
Woodstock Soapstone Company and Rais also provide an example each of a
woodstove that has one of the lowest weighted average emissions of all
EPA-certified woodstoves, but due to one test run exceeding 6 grams per
hour, would not be approved for sale in the Fairbanks PM2.5
Nonattainment Area.
Another anonymous commenter states that non-catalytic stoves are
more user-friendly and require less maintenance, but they are more
likely to be rejected under this one-hour requirement because non-
catalytic stoves require more heat to burn cleanly, and they take time
to heat up and start burning cleanly. Hearth & Home Technologies, Inc.
asserts that the clearest path to cleaner air in the Fairbanks
PM2.5 Nonattainment Area is by removing older, pre-1988
wood-burning devices, not by prohibiting certain EPA-certified devices
that do not meet Alaska's revised requirements in 18 AAC 50.077.
Response 1: For the ensuing reasons, the comments do not
demonstrate that approval of Alaska's revisions to 18 AAC 50.077 is
inconsistent with the CAA; therefore, the EPA is finalizing its
approval as proposed. Regarding Alaska's rule revisions for wood-fired
heating device emission standards under 18 AAC 50.077, the EPA proposed
to find that the revisions submitted by ADEC are more stringent than
the current EPA-approved rules. For the reasons stated in our proposal
and in this response, we find that Alaska was not unreasonable in
requiring additional testing requirements as a method of regulating the
installation and operation of woodstoves. As stated in a prior EPA
action on November 27, 2018 (83 FR 60769), approving the Alaska SIP as
meeting specific infrastructure requirements for the 1997, 2006, and
2012 PM2.5 NAAQS, the EPA disagrees with the premise that
states cannot regulate a source category more stringently than may be
required in a Federal regulation. The EPA's role is to review and
approve state choices if they meet the CAA requirements. There is
nothing in the CAA that prevents SIP provisions from being more
stringent than Federal NSPS standards. To the contrary, CAA section 116
explicitly authorizes states to regulate sources more stringently than
the EPA does through Federal regulations. Thus, the fact that 18 AAC
50.077 is more stringent than the NSPS for new residential wood heaters
does not impact the approvability of these control measures as SIP-
strengthening.
In addition, ADEC addressed similar comments during the State's
public comment period on the SIP revisions. In the Alaska Department of
Environmental Conservation's Response to Comments on the proposed
regulations (ADEC Response to Comments),\2\ ADEC asserted that the
purpose of these additional testing requirements is to better reflect
actual emissions of wood heaters in the Fairbanks PM2.5
Nonattainment Area.
[[Page 52999]]
ADEC asserted that the current test method for woodstoves that results
in the certification value (grams of PM2.5 per hour)
averages emissions over four steady-state runs. The values from each of
these runs is an average emission rate over the time it takes to burn
100% of the full load of wood used for each run. This approach
translates into a certification value that is an average of an average.
ADEC stated that averaging results multiple times minimizes emission
rates, which results in certification values that may vastly under
predict actual in-use emission rates and does not reflect the fuel
loading events that in field use may occur multiple times per day.
Further, ADEC stated that real-time PM2.5 measurements
collected from EPA certification tests have shown that the maximum
emission rate occurs within two hours of the test period, and
typically, on average, appliances spend approximately 50% of the
certification testing time in the period known as the charcoal tail,
where virtually no emissions occur, and in some cases filters may
experience particulate loss due to warm dry air blowing through the
filter. While this test method approach differs from the NSPS for new
residential wood heaters, EPA finds ADEC's rationale for the revisions
to 18 AAC 50.077 is reasonable and a rational attempt to strengthen
rules for the residential space heating source category.
---------------------------------------------------------------------------
\2\ Alaska Department of Environmental Conservation, Response to
Comments on May 14, 2019, Proposed Regulations, November 19, 2019.
Pages 37-38, 51-53.
---------------------------------------------------------------------------
With respect to the inclusion of the TEOM measurement requirement,
ADEC states that the goal was to achieve a 1.0 grams per hour emission
limit in practice, taking into consideration the variability of
emissions when burning cordwood. After reviewing public comments
submitted during the State's public comment period, ADEC amended the
final regulation to provide an alternative to the TEOM test method
while still providing what it considered to be an equivalent, if not
better, air quality result than a 1.0 grams per hour average emission
limit. The final regulation stipulates that manufacturers may provide
the TEOM data as ADEC originally proposed, with the additional
specificity that no rolling 60-minute period may exceed 4.0 grams per
hour, or alternatively, by utilizing existing EPA certification test
data showing that no valid one-hour filter measurement from the
certifying report to EPA is greater than 6.0 grams per hour.
ADEC asserted that, while this limit is three times the final ADEC
standard (certification value of 2.0 grams per hour or less), the limit
will apply to all woodstoves being installed, reinstalled, sold,
leased, distributed, or conveyed in the nonattainment area (not just
non-catalytic devices). Due to a number of devices expected to exceed
this limit based on the revised test method, the result will be fewer
devices available for installation, sale, lease, distribution, or
conveyance in the area. ADEC noted this approach is designed to ensure
that performance of the devices under more real-world operations will
be more consistent because the emissions limit value is not an average.
As an example, ADEC found devices that meet the 1.0 grams per hour
emissions limit (adopted in Missoula County, Montana), but that exceed
the one-hour filter measurement of 6.0 grams per hour.
Further, ADEC noted that, while the TEOM is a new approach for wood
heater device certification testing, it has been incorporated into a
standard test method (ASTM D6831-11) for stack gas testing. ADEC
believes the TEOM test is a valuable tool that should be used in future
device certification test requirements and has maintained it as one
option for meeting testing requirements in the final regulation. ADEC
stated that it is specifying use of the TEOM and its alternative one-
hour filter measurement is based on the ADEC's analysis of over 60 EPA
approved certification reports, the vast majority of the tests reviewed
were for EPA Step 2 certification.
Thus, Alaska developed and implemented additional requirements for
wood-fired heating devices, a 2.0 grams per hour limit for all wood-
fired devices and hourly requirements measured by a TEOM device or
during the EPA certification process, with the intention to reduce the
emissions from the home heating source category, the source category
with the highest PM2.5 emissions in the Fairbanks
PM2.5 Nonattainment Area. EPA has determined that Alaska's
revisions to 18 AAC 50.077 are reasonable and strengthen the SIP with
respect to the regulation of emissions from the residential space
heating source category.
Comment 2: HPBA, Kozy Heat Fireplaces, and Travis Industries assert
that the one-hour filter alternative is not compatible with woodstove
emissions and the Federal air quality standard that the EPA based on
data averaged over 24 hours, noting that the Federal air quality
standard is not a ``peaking'' standard that is violated by a single
episodic, one-hour reading. Thus, the commenters assert that the EPA
was proposing to approve this metric without any explanation in the
record of its relevance to the nonattainment issues experienced in the
Fairbanks PM2.5 Nonattainment Area.
Response 2: The EPA disagrees with the commenters. First, the EPA
disagrees with the commenters' assertion that device requirements must
be directly tied to the Federal air quality standard. Overall, the EPA
notes that PM2.5 is a complex and highly variable mixture of
particles and gases. The EPA's PM2.5 Implementation Rule (81
FR 58010, August 24, 2016) recommends that states should base potential
control measures in part on an analysis of emissions inventory data
summaries, fine particle speciation monitoring data, and source
apportionment air quality modeling data. Emissions standards can have
different averaging periods based on the type of source, rate of
emissions, and control measure. Irrespective of the particular NAAQS,
our basis for approval here is that Alaska's revisions to 18 AAC 50.077
render the SIP more stringent than the prior approved rule in terms of
regulating emissions from woodstoves. The EPA finds that ADEC's
rationale for why the revised 18 AAC 50.077 will reduce emissions from
the residential home heating source category is reasonable.
Second, the record contains ample information showing that ADEC's
revised rule will reduce emissions of direct PM2.5 from the
residential home heating source category. The EPA evaluated ADEC's SIP
submission, including the responses to similar comments in the
development of the State's regulation. In ADEC's Response to Comments,
ADEC noted that, under the 2015 NSPS for new residential wood heaters,
the EPA required reporting of emission rates for the first hour of the
test period. This data reflects the timing and emission rates typically
associated with the 60-minute test requirements for particulate matter
testing at all other sources (EPA Method 5). ADEC asserted that the
assessment of one-hour data allows agencies to gauge performance and
determine which appliances are low emitting from the start of the
certification test versus those that have been able to design for long
charcoal tails to minimize the peak emissions. ADEC additionally stated
that one of the reasons for requiring the use of TEOM measurement data
is to provide a more meaningful equivalency to a 1.0 grams per hour
average emission limit (as adopted by Missoula County, Montana), taking
into consideration the variability of emissions when burning cordwood,
while still allowing a range of devices to be sold and used in the
Fairbanks PM2.5 Nonattainment Area. Thus, the record does
contain information
[[Page 53000]]
explaining the reason for the one-hour filter alternative.
Finally, as stated in a prior EPA action on November 27, 2018 (83
FR 60769), approving the Alaska SIP as meeting specific
PM2.5 infrastructure requirements, states have the
obligation to regulate sources as necessary to meet nonattainment area
plan stringency requirements, such as reasonably and best available
control measures, and the obligation to regulate sources as necessary
to attain the NAAQS in a given nonattainment area. ADEC determined it
was necessary to revise 18 AAC 50.077 and submitted the revisions to
address Serious area planning requirements for best available control
measures in the Fairbanks PM2.5 Nonattainment Area. While
this action does not address whether the submitted revisions to 18 AAC
50.077 and other rules are sufficient to meet best available control
measure requirements, we explained in our proposed action how the
revisions strengthen the SIP. The comments do not demonstrate that
Alaska's revisions to 18 AAC 50.077 or rationale for these revisions
are unreasonable, and EPA is thus finalizing approval of 18 AAC 50.077
as proposed.
Comment 3: HPBA, Blaze King Industries, Inc., Hearth & Home
Technologies, Inc., Travis Industries, and United States Stove Company
note that Fairbanks has a unique winter environment where woodstoves
are only ``started'' once during winter and left running during entire
cold season. Thus, the commenters assert that establishing a
particulate emissions standard based only on the first hour of
operation inaccurately represents the emissions of wood-fired heating
devices in the Fairbanks PM2.5 Nonattainment Area. In
addition, Blaze King Industries, Inc. states that woodstove users in
the Fairbanks North Star Borough are unique in their use of stoves to
address sub-zero climate conditions in the region. Myren Consulting
states that, no matter the test method, testing of certified stoves in
the test environment will not reflect conditions in the field because
of differences in static pressure, that the commenter asserts will
significantly affect performance in areas with colder temperatures such
as in Fairbanks.
Response 3: As noted in Responses 1 and 2, ADEC revised 18 AAC
50.077 to reduce emissions from wood-fired heating devices while
allowing for sale and use of a range of devices in the Fairbanks
PM2.5 Nonattainment Area. In ADEC's Response to Comments,
ADEC stated that the TEOM measurement and the one-hour filter pull data
reflect more real-time particulate matter measurements and that other
test methods, based on an average of multiple test runs, may vastly
under predict actual in-use emission rates and do not reflect the
actual fuel loading events that may occur multiple times per day.
Moreover, ADEC developed this control measure as part of its control
measure analysis that incorporates the emissions inventory, speciation,
and source apportionment data for the nonattainment area. Based on
ADEC's SIP submission, including the responses to comments in ADEC's
rulemaking process, the EPA finds that ADEC's rationale for
incorporating the TEOM measurement and the one-hour filter pull data is
credible and based on a robust understanding of the emissions from
woodstoves. Therefore, the EPA is approving this rule revision as SIP-
strengthening because the revised rule imposes requirements for
woodstoves in the Fairbanks PM2.5 Nonattainment Area that
are more stringent than the woodstove requirements in the current SIP.
Comment 4: Travis Industries asserts that the EPA must expressly
state that the standards ADEC is imposing in 18 AAC 50.077 are
inappropriate in other settings that do not share the Fairbanks
PM2.5 Nonattainment Area's extreme climatic conditions.
Response 4: As specified in 18 AAC 50.077, this regulation only
applies to qualifying wood-fired heating devices in areas in Alaska
that are designated nonattainment for PM2.5, under 18 AAC
50.015(b)(3). Currently the Fairbanks and North Pole urban area (i.e.,
Fairbanks PM2.5 Nonattainment Area) is listed as the only
nonattainment area in Alaska where this regulation applies. However,
other state and local governments have the authority to adopt similar
measures.
Comment 5: Comments by HPBA, Blaze King Industries, Inc., Kuma
Stoves, Inc., IHP, Woodstock Soapstone Company, Myren Consulting, and
FPI object to Alaska's authority to validate the EPA's wood-fired
heating device certifications for applicability in the Fairbanks
PM2.5 Nonattainment Area and limit the EPA-approved
applicable testing methods. HPBA asserts that, under 18 AAC
50.077(c)(3)(A), ADEC can effectively veto an EPA device certification
on the grounds that ADEC had not approved the same alternative test
method. As an example, HPBA notes that while the EPA approved ASTM 3053
(cordwood test method), Alaska has not. These commenters state that
Alaska's failure to recognize this approved test method undermines the
EPA's authority. In addition, Kuma Stoves, Inc. states that the EPA
should not now, after benefitting from valuable data generated by the
ASTM 3053 test method, support language that declares ASTM 3053 to be a
nonrepresentative test. One anonymous commenter contends that, based on
experience as a manufacturer of EPA-certified woodstoves, the ASTM 3053
test method is credible and produces consistent and reliable emissions
values, and therefore rejecting this test method results in less
informative testing data.
Generally, IHP states that it is onerous for a state to regulate an
industry to meet any requirements that are not previously set and known
before development, certification, and manufacturing of those industry
products. Kozy Heat Fireplaces, Inc. states these device requirements
impose new and greater costs for certification and that these costs
have not been quantified by either ADEC or the EPA. IHP recommends that
the EPA reject ADEC's revised requirements for woodstoves in the Alaska
SIP submission as a ``de facto federal standard,'' and in the comment
encourages the State of Alaska to work with the industry to find a more
complete solution. FPI also notes that, not only does ADEC not
recognize the alternate test method, but it does not recognize the 2.5
grams per hour emissions limit associated with this test method. FPI
asserts that dismissing this limit by setting a 2.0 grams per hour
limit for cordwood without a scientific process and peer review is
arbitrary.
An anonymous commenter notes that the same entities are involved in
woodstove device testing certifications and accreditations as product
safety testing. The commenter states that laboratories need an
International Organization for Standardization (ISO) 17025
accreditation that can be renewed every two years following an official
audit from the accreditor. The commenter states that proficiency
testing has been put in place by the EPA as part of the ISO-17025
accreditation and all accredited laboratories should comply with the
proficiency testing every two years.
Response 5: The EPA disagrees with the commenters' assertion that
Alaska lacks authority to promulgate rules that are more stringent than
EPA's NSPS or that otherwise limit the range of devices allowed in the
area. The EPA also disagrees with the assertion that Alaska, by
promulgating these rules, establishes a ``de facto federal standard''
and as such undermines the EPA's independent authorities to establish
Federal new source performance standards. Congress gave the EPA
[[Page 53001]]
authority in CAA section 111 to establish performance standards for
categories of new sources. Distinct from CAA section 111, Congress
required in CAA section 110 that states have an overarching SIP to
implement, maintain, and enforce the NAAQS. If states have designated
nonattainment areas, then they must make a nonattainment plan SIP
submission meeting additional specific requirements. State regulation
of sources more stringently for purposes of meeting SIP requirements
does not interfere or undermine the EPA's authority to regulate new
sources under the CAA. With few exceptions, states are not preempted
from regulating source categories more stringently and have explicit
authority in CAA section 116 to do so.
The EPA disagrees with the commenters' assertion that ADEC did not
consider compliance costs. In ADEC's Response to Comments, Alaska
acknowledged the potential increased costs to certification testing.
ADEC stated that the intention is to provide a meaningful equivalent
control measure to a 1.0 grams per hour average emissions limit, while
also allowing a range of devices to be sold and used in the Fairbanks
PM2.5 Nonattainment Area. As discussed in Response 1 in this
preamble, states have explicit authority to regulate a source category
more stringently than may be required in a Federal regulation. The
EPA's role is to review and approve state choices if they meet
applicable CAA requirements. See 42 U.S.C. 7410(k) and 40 CFR 52.02(a);
see also Union Elec. Co. v. EPA, 427 U.S. 246, 256-266 (1976) (holding
that the EPA may not disapprove a state implementation plan that meets
the requirements of CAA Section 110(a)(2) on the basis of technological
or economic infeasibility). There is nothing in the CAA that prevents
states from imposing SIP requirements that are more stringent than
Federal NSPS standards.
Regarding woodstove device testing certifications and ISO-17025
accreditations, the 2015 NSPS stipulates that for new residential wood
heaters, new residential hydronic heaters, and forced-air furnaces (80
FR 13672), a test laboratory must agree to participate biennially in an
independently operated proficiency testing program with no direct ties
to the participating laboratories. Further, the EPA Administrator may
revoke a test laboratory approval if a test laboratory has failed to
participate in a proficiency testing program, in accordance with 40 CFR
60.535.
Comment 6: Central Boiler/Woodmaster objects to the provision under
18 AAC 50.077(a) that prohibits the sale and installation of cordwood-
fueled outdoor hydronic heaters in the Fairbanks PM2.5
Nonattainment Area. Central Boiler/Woodmaster states that these devices
are not given consideration by the state based on emissions or
performance like other wood heating appliances.
Response 6: Consistent with CAA requirements and the EPA's
PM2.5 Implementation Rule, Alaska has authority to prohibit
the sale and installation of devices that contribute to
PM2.5 concentrations in the Fairbanks PM2.5
Nonattainment Area, such as cordwood-fueled outdoor hydronic heaters,
to bring the area into attainment. We note that, under 18 AAC
50.077(b), Alaska does permit pellet-fueled wood-fired hydronic heaters
for use in the Fairbanks PM2.5 Nonattainment Area, if
specific device performance criteria meet Alaska regulations.
Therefore, the EPA is finalizing the approval of 18 AAC 50.077(b) as
proposed.
Comment 7: HPBA notes that while point sources (electric power
plants) constitute the largest source of SO2 emissions in
the Fairbanks PM2.5 Nonattainment Area, ADEC, in many
instances, did not require additional source-level controls on several
large facilities. HPBA states that ADEC did not require installation of
new control technologies for SO2 even though the average
daily emissions from these point sources are nearly three times larger
than sources of directly-emitted PM2.5 from woodstoves.
Response 7: The EPA agrees with the commenter that the largest
source category of SO2 emissions is point sources, including
electric power plants, and that SO2 is a significant
contributor to PM2.5 concentrations in the Fairbanks
PM2.5 Nonattainment Area. On December 13, 2019, Alaska
submitted a best available control technology (BACT) control analysis
for specific point sources located in the area, including several
electric power plants, as part of the Fairbanks Serious Plan. However,
we consider this comment to be outside the scope of this action. In
this action, the EPA is evaluating rule revisions that ADEC has adopted
to address direct PM2.5 emissions from wood-fired heating
devices. We did not propose action on the BACT Serious area planning
requirements, including the issue of appropriate regulation of
SO2 emissions from point sources, as part of this action. We
intend to address Alaska's best available control measures (BACM)/BACT
control analysis, and any supplemental BACT control analysis
submissions, in a separate action. We encourage the commenter to
resubmit the comment during the public comment period of our future
action on the BACT control analysis.
Conclusion
The EPA finds that the comments do not change our proposed
determination that the regulations submitted by Alaska are consistent
with CAA requirements and strengthen the SIP. Therefore, we are
finalizing our action as proposed.
III. Final Action
In this action, the EPA is approving a portion of the submitted
revisions to the Alaska SIP as meeting the following Serious Plan
required elements for the Fairbanks PM2.5 Nonattainment
Area:
The 2013 base year emissions inventory (CAA section
172(c)(3); 40 CFR 51.1008(b)(1)); and
The State's PM2.5 precursor demonstration for
NOX and volatile organic compound (VOC) emissions (CAA
section 189(e); 40 CFR 51.1006(a)).
We reiterate that Alaska's precursor analysis did not address
nonattainment New Source Review (NSR) requirements. The State made the
prior determination to regulate all four EPA identified legal
precursors to PM2.5 in the nonattainment NSR regulations
applicable to the Fairbanks PM2.5 Nonattainment Area. The
EPA approved Alaska's October 25, 2018, SIP revision as meeting the
nonattainment NSR requirements triggered upon reclassification of the
area to Serious (August 29, 2019, 84 FR 45419).
Specifically, the EPA is approving the submitted sections of the
Alaska Air Quality Control Plan for the Fairbanks PM2.5
Nonattainment Area, State effective January 8, 2020:
Volume II Section III.D.7.06 and Volume III Section
III.D.7.06 Emissions Inventory, for purposes of the 2013 base year
emissions inventory;
Volume II Section III.D.7.08 Precursor Demonstration, for
the purposes of NOX and VOC emissions as it relates to BACM/
BACT control measure requirements; and
Further, the EPA is approving the submitted section of the Alaska
Air Quality Control Plan for the Fairbanks PM2.5
Nonattainment Area, State effective December 25, 2020:
Volume II Section III.D.7.12, Emergency Episode Plan.\3\
---------------------------------------------------------------------------
\3\ Submitted on December 15, 2020 and included in the docket.
The EPA is not at this time determining whether this updated
planning chapter, in conjunction with the associated regulatory
changes, meets other Serious area nonattainment plan requirements
for the 2006 24-hour PM2.5 NAAQS in the Fairbanks
PM2.5 Nonattainment Area.
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[[Page 53002]]
In addition, the EPA is approving and incorporating by reference
the submitted regulatory changes listed below into the Alaska SIP. As
stated in our proposal, the EPA is not at this time determining whether
these provisions also meet other Serious area nonattainment plan
requirements for the Fairbanks PM2.5 Nonattainment Area.
Upon the effective date of this action, the Alaska SIP will include:
18 AAC 50.030, except (a), State effective January 12,
2018;
18 AAC 50.075, except (d)(2) and (f), State effective
January 8, 2020;
18 AAC 50.076, except (g)(11), State effective January 8,
2020;
18 AAC 50.077, except (g) and (q), State effective January
8, 2020;
18 AAC 50.078, except (c) and (d), State effective January
8, 2020;
18 AAC 50.079, except (e), State effective January 8,
2020; and
18 AAC 50.990(71), (138), (149), (150), (151), (152),
(153), (154), and (155), State effective January 8, 2020.
IV. Incorporation by Reference
In this document, the EPA is finalizing regulatory text in an EPA
final rule that includes incorporation by reference. In accordance with
requirements of 1 CFR 51.5, the EPA is finalizing the incorporation by
reference the regulations described in Section III of this preamble.
The EPA has made, and will continue to make, these materials generally
available through https://www.regulations.gov and at the EPA Region 10
Office (please contact the person identified in the FOR FURTHER
INFORMATION CONTACT section of this preamble for more information).
Therefore, these materials have been approved by the EPA for
inclusion in the State implementation plan, have been incorporated by
reference by the EPA into that plan, are fully federally enforceable
under sections 110 and 113 of the CAA as of the effective date of the
final rulemaking of the EPA's approval, and will be incorporated by
reference by the Director of the Federal Register in the next update to
the SIP compilation.
V. Statutory and Executive Order Reviews
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA 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);
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 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 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. 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 ``major rule'' as defined by 5 U.S.C.
804(2).
Under section 307(b)(1) of the Clean Air Act, petitions for
judicial review of this action must be filed in the United States Court
of Appeals for the appropriate circuit by November 23, 2021. 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 in 40 CFR Part 52
Environmental protection, Air pollution control, Carbon monoxide,
Incorporation by reference, Intergovernmental relations, Lead, Nitrogen
dioxide, Ozone, Particulate matter, Reporting and recordkeeping
requirements, Sulfur oxides, Volatile organic compounds.
Dated: September 15, 2021.
Michelle L. Pirzadeh,
Acting Regional Administrator, Region 10.
For the reasons set forth in the preamble, 40 CFR part 52 is
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 C--Alaska
0
2. In Sec. 52.70:
0
a. The table in paragraph (c) is amended by:
0
i. Adding the entry ``18 AAC 50.030'' in numerical order;
0
ii. Revising the entries ``18 AAC 50.075'', ``18 AAC 50.076'', and ``18
AAC 50.077'';
0
iii. Adding the entries ``18 AAC 50.078'' and ``18 AAC 50.079'' in
numerical order; and
0
iv. Revising the entry ``18 AAC 50.990''.
[[Page 53003]]
0
b. The table in paragraph (e) is amended by adding the entries
``II.III.D.7.06 Fairbanks Emissions Inventory Data'', ``III.III.D.7.06
Appendix to Fairbanks Emissions Inventory Data'', ``II.III.D.7.08
Fairbanks Modeling'', and ``II.III.D.7.12 Fairbanks Emergency Episode
Plan'' to the end of the table.
The additions and revisions read as follows:
Sec. 52.70 Identification of plan.
* * * * *
(c) * * *
EPA-Approved Alaska Regulations and Statutes
----------------------------------------------------------------------------------------------------------------
State
State citation Title/subject effective EPA approval date Explanations
date
----------------------------------------------------------------------------------------------------------------
Alaska Administrative Code Title 18 Environmental Conservation, Chapter 50--Air Quality Control (18 AAC 50)
18 AAC 50--Article 1. Ambient Air Quality Management
* * * * * * *
18 AAC 50.030................. State Air Quality 1/12/2018 9/24/2021, [Insert Except (a).
Control Plan. Federal Register
citation].
* * * * * * *
18 AAC 50.075................. Solid Fuel-Fired 1/8/2020 9/24/2021, [Insert Except (d)(2) and
Heating Device Federal Register (f).
Visible Emission citation].
Standards.
18 AAC 50.076................. Solid Fuel-Fired 1/8/2020 9/24/2021, [Insert Except (g)(11).
Heating Device Fuel Federal Register
Requirements; citation].
Requirements for
Wood Sellers.
18 AAC 50.077................. Standards for Wood- 1/8/2020 9/24/2021, [Insert Except (g) and (q).
Fired Heating Federal Register
Devices. citation].
18 AAC 50.078................. Additional Control 1/8/2020 9/24/2021, [Insert Except (c) and (d).
Measures for a Federal Register
Serious PM2.5 citation].
Nonattainment Area.
18 AAC 50.079................. Provisions for Coal- 1/8/2020 9/24/2021, [Insert Except (e).
Fired Heating Federal Register
Devices. citation].
* * * * * * *
18 AAC 50--Article 9. General Provisions
* * * * * * *
18 AAC 50.990................. Definitions.......... 1/8/2020 9/24/2021, [Insert
Federal Register
citation].
* * * * * * *
----------------------------------------------------------------------------------------------------------------
* * * * *
(e) * * *
EPA-Approved Alaska Nonregulatory Provisions and Quasi-Regulatory Measures
----------------------------------------------------------------------------------------------------------------
State
Name of SIP provision Applicable geographic submittal EPA approval date Explanations
or nonattainment area date
----------------------------------------------------------------------------------------------------------------
* * * * * * *
Recently--Approved Plans
* * * * * * *
II.III.D.7.06 Fairbanks Fairbanks North Star 12/13/2019 9/24/2021, [Insert Approved for purposes
Emissions Inventory Borough. Federal Register of the Fairbanks
Data. citation]. Serious Plan 2013 base
year emissions
inventory.
III.III.D.7.06 Appendix Fairbanks North Star 12/13/2019 9/24/2021, [Insert Approved for purposes
to Fairbanks Emissions Borough. Federal Register of the Fairbanks
Inventory Data. citation]. Serious Plan 2013 base
year emissions
inventory.
II.III.D.7.08 Fairbanks Fairbanks North Star 12/13/2019 9/24/2021, [Insert Approved for purposes
Modeling. Borough. Federal Register of the Fairbanks
citation]. Serious Plan PM2.5
precursor
demonstration for NOX
and VOC emissions as
it relates to BACM/
BACT control measure
requirements.
[[Page 53004]]
II.III.D.7.12 Fairbanks Fairbanks North Star 12/15/2020 9/24/2021, [Insert
Emergency Episode Plan. Borough. Federal Register
citation].
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[FR Doc. 2021-20396 Filed 9-23-21; 8:45 am]
BILLING CODE 6560-50-P