Air Plan Approval; AK: Interstate Transport Requirements for the 2015 Ozone Standard, 69331-69335 [2019-27162]
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Federal Register / Vol. 84, No. 243 / Wednesday, December 18, 2019 / Rules and Regulations
Rulemaking Requirements
Administrative Procedure Act: This
final rule revises the effective date of the
July 31, 2019 final rule implementing
procedures requiring the electronic
filing of trademark applications and all
submissions associated with trademark
applications and registrations, and the
subsequent correction rule published on
December 13, 2019, and it is a rule of
agency practice and procedure, and/or
interpretive rules pursuant to 5 U.S.C.
553(b)(A). See JEM Broad. Co. v. F.C.C.,
22 F.3d 32. (D.C. Cir. 1994) (‘‘[T]he
‘critical feature’ of the procedural
exception [in 5 U.S.C. 553(b)(A)] ‘is that
it covers agency actions that do not
themselves alter the rights or interests of
parties, although [they] may alter the
manner in which the parties present
themselves or their viewpoints to the
agency.’’’ (quoting Batterton v. Marshall,
648 F.2d 694, 707 (D.C. Cir. 1980))); see
also Bachow Commc’ns Inc. v. F.C.C.,
237 F.3d 683, 690 (D.C. Cir. 2001) (rules
governing an application process are
procedural under the Administrative
Procedure Act); Inova Alexandria Hosp.
v. Shalala, 244 F.3d 342, 350 (4th Cir.
2001) (rules for handling appeals were
procedural where they did not change
the substantive standard for reviewing
claims). Accordingly, prior notice and
opportunity for public comment are not
required pursuant to 5 U.S.C. 553(b) or
(c) (or any other law). See Cooper Techs.
Co. v. Dudas, 536 F.3d 1330, 1336–37
(Fed. Cir. 2008) (stating that 5 U.S.C.
553, and thus 35 U.S.C. 2(b)(2)(B), does
not require notice and comment
rulemaking for ‘‘interpretative rules,
general statements of policy, or rules of
agency organization, procedure, or
practice’’ (quoting 5 U.S.C. 553(b)(A)).
Moreover, the Director of the USPTO,
pursuant to authority at 5 U.S.C.
553(b)(B), finds good cause to adopt the
change in this final rule without prior
notice and an opportunity for public
comment, as such procedures would be
impracticable and contrary to the public
interest. Immediate implementation of
the delay in effective date is in the
public interest, because it is responsive
to recent feedback received from
external stakeholders regarding their
need to more fully comprehend the
nature of, and prepare to comply with,
the new requirements before they are
effective. It will also allow the USPTO
additional time to ensure that internal
implementation of the requirements
associated with the July 31, 2019 final
rule and the December 13, 2019
correction is in place. Delay of the July
31, 2019 final rule and the December 13,
2019 correction to provide prior notice
and comment procedures is
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impracticable, because it would allow
the July 31, 2019 final rule and
December 13, 2019 correction to go into
effect before external stakeholders are
ready to comply with, and the agency is
ready to implement, the new
requirements. Therefore, the Director
finds there is good cause to waive notice
and comment procedures for this rule.
Finally, the change in this final rule
may be made effective earlier than the
required 30-day delay in effectiveness
because this is not a substantive rule
under 35 U.S.C. 553(d). Moreover,
pursuant to 5 U.S.C. 553(d)(3), the
Director finds good cause to waive the
30-day delay in effectiveness for this
final rule because such a delay would
allow the July 31, 2019 final rule and
December 13, 2019 correction to go into
effect before external stakeholders are
ready to comply with, and the agency is
ready to implement, the new
requirements.
69331
Dated: December 16, 2019.
Andrei Iancu,
Under Secretary of Commerce for Intellectual
Property and Director of the United States
Patent and Trademark Office.
The EPA has established a
docket for this action under Docket ID
No. EPA–R10–OAR–2018–0823. All
documents in the docket are listed on
the https://www.regulations.gov
website. Although listed in the index,
some information is not publicly
available, e.g., Confidential Business
Information or other information the
disclosure of which is restricted by
statute. Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available at https://
www.regulations.gov, or please contact
the person listed in the FOR FURTHER
INFORMATION CONTACT section for
additional availability information.
FOR FURTHER INFORMATION CONTACT:
Kristin Hall (15–H13), Air and Radiation
Division, EPA Region 10, 1200 Sixth
Avenue (Suite 155), Seattle, WA 98101,
(206) 553–6357, hall.kristin@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document wherever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, it refers
to the EPA.
[FR Doc. 2019–27426 Filed 12–17–19; 8:45 am]
Table of Contents
BILLING CODE 3510–16–P
I. Background
II. Response to Comment
III. Final Action
IV. Statutory and Executive Order Review
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R10–OAR–2018–0823; FRL–10003–
24–Region 10]
Air Plan Approval; AK: Interstate
Transport Requirements for the 2015
Ozone Standard
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Clean Air Act requires
each State Implementation Plan (SIP) to
contain adequate provisions prohibiting
emissions that will have certain adverse
air quality effects in other states. On
October 25, 2018, the State of Alaska
made a submission to the
Environmental Protection Agency (EPA)
to address these requirements for the
2015 ozone National Ambient Air
Quality Standards (NAAQS). The EPA
approves the Alaska SIP as meeting the
requirement that each SIP contain
adequate provisions to prohibit
emissions that will significantly
contribute to nonattainment or interfere
with maintenance of the 2015 ozone
NAAQS in any other state.
DATES: This final rule is effective
January 17, 2020.
SUMMARY:
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ADDRESSES:
I. Background
On October 25, 2018, the Alaska
Department of Environmental
Conservation (ADEC) made a
submission addressing the interstate
transport requirements of CAA section
110(a)(2)(D)(i)(I) for the 2015 ozone
NAAQS.1 This ‘‘good neighbor’’
provision of the CAA requires that a SIP
for a new or revised NAAQS must
contain adequate provisions prohibiting
any source or other type of emissions
activity within the State from emitting
air pollutants in amounts that will
significantly contribute to
nonattainment of such NAAQS in any
other state or that will interfere with
maintenance of the NAAQS in any other
state.
On June 5, 2019, we proposed to
approve Alaska’s SIP submission (84 FR
26041). The reasons for our proposed
approval are included in the proposed
1 Alaska’s October 25, 2018 submission addresses
all CAA sections 110(a)(1) and (2) infrastructure
requirements for the 2015 ozone NAAQS (including
interstate transport prongs 1 and 2) and includes
regulatory updates and permitting rule revisions for
approval into the SIP. This action addresses the
portion of the submission related to interstate
transport prongs 1 and 2. We are addressing the
remainder of the submission in separate actions on
August 29, 2019 (84 FR 45419) and October 15,
2019 (84 FR 55094).
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action and will not be restated here. The
public comment period for the proposed
action closed on July 5, 2019. We
received adverse comments from one
anonymous commenter. Following is
our response to each distinct issue
raised by the commenter.
II. Response to Comment
Comment 1: The commenter stated
that the EPA should not approve
Alaska’s SIP submission because ADEC
did not model Alaska emissions and the
effect of those emissions on other states
and Canada.
Response 1: The commenter is correct
that ADEC did not model Alaska
emissions and the effect of those
emission on other states and Canada.
However, that is not a basis for
disapproval in this instance. Alaska’s
SIP submission included information
and analysis on the amount and sources
of ozone precursor emissions from
Alaska, trends in monitored ambient
ozone levels, meteorological conditions,
distances from Alaska to the nearest
receptors in other states, and
intervening geography that isolates
Alaska from other areas that have ozone
problems. ADEC concluded that
emissions from Alaska sources do not
significantly contribute to
nonattainment of the 2015 ozone
NAAQS in any other state and do not
interfere with maintenance of the 2015
ozone NAAQS in any other state.
In our review, we evaluated Alaska’s
SIP submission and conducted our own
weight of evidence analysis to
determine whether we agreed with
ADEC’s conclusion. We assessed
emissions inventory data, monitoring
trends, geography, meteorology, and
current SIP-approved provisions. We
found these factors sufficiently
informative regarding Alaska’s potential
to adversely impact air quality in
downwind states without conducting
modeling of emissions as suggested by
the commenter, and therefore, proposed
to approve the SIP submission. We note
this is not a new approach. The EPA has
conducted weight of evidence analyses
to evaluate prior Alaska interstate
transport SIP submissions, and we
believe it to be a reasonable and
appropriate approach in this instance.2
The EPA further agrees that ADEC did
not analyze potential transport to
Canada, but that is not a deficiency in
the State’s analysis. The evaluation of
international air quality impacts is not
a requirement under CAA section
2 Most
recently, we took this approach in our June
27, 2018 action approving the Alaska SIP for
purposes of CAA section 110(a)(2)(D)(i)(I) with
respect to the 2012 fine particulate matter NAAQS
(83 FR 30048).
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110(a)(2)(D)(i)(I), which is the only
provision of the statute addressed in
this action.3
Comment 2: The commenter stated,
‘‘the EPA can’t rely on relative
emissions to justify [a finding of] no
significant contribution or interference
with maintenance’’ of the 2015 ozone
NAAQS. The commenter also noted
that, in our proposal, we showed that
nitrogen oxide (NOX) emissions from
certain Alaska sources ranked second
highest in the region.
Response 2: The commenter is correct
that, based on the 2014 National
Emissions Inventory (2014 NEI), NOX
emissions from mobile and stationary
sources in Alaska ranked second highest
of the Region 10 states.4 Our analysis,
however, also compared Alaska
emissions to those nationwide and
determined that, based on the 2014 NEI,
NOX emissions from Alaska mobile and
stationary sources totaled just one
percent of national NOX emissions.5
This comparison of relative emissions
puts Alaska emissions estimates into
context and is a useful exercise in
evaluating the Alaska ozone interstate
transport SIP submission. Importantly,
this was just one factor in our weight of
evidence analysis and was considered
in conjunction with other factors
including monitoring trends, geography,
meteorology, and current SIP-approved
provisions. In particular, the fact that
other, geographically-closer states with
comparable or greater emission levels
did not impermissibly impact
downwind air quality problems
supports the conclusion that Alaska
emissions are not likely to be linked to
identified nonattainment and
maintenance receptors in any other state
with respect to the 2015 ozone NAAQS.
We continue to find this to be true.
Comment 3: The commenter took
issue with the EPA’s evaluation of instate monitored ozone levels. The
commenter asserted that in-state levels
are not predictive of downwind levels.
Response 3: We found it informative
to review in-state monitored ozone
levels as part of our weight of evidence
analysis. This kind of information can
shed light on whether in-state
conditions are changing and whether
3 CAA sections 110(a)(2)(D)(ii) and 115 address
international pollution abatement. We proposed
approval of this element for the 2015 ozone NAAQS
in a separate action on October 15, 2019 (84 FR
55094). Alaska has no pending obligations under
CAA section 115 with respect to Canada or any
other foreign country.
4 Alaska’s stationary and mobile source NO
X
emissions were estimated to be 127,194 tons.
Washington’s emissions were higher (234,050 tons),
while Oregon and Idaho’s emissions are somewhat
lower (125,626 and 81,135 tons, respectively).
5 Based on the 2014 NEI.
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those changes could have downwind
implications. For example, if ozone
levels at monitoring sites in Alaska were
rising over time, it could suggest
increased precursor emissions from
Alaska sources which could also have
impacts on downwind air quality in
other states. In our proposal, we
assessed monitored ozone trends in
Alaska and determined that in-state
ozone levels were well below the 2015
ozone NAAQS. The table of design
values in our proposal illustrated that
trends have been generally flat from
2010 to 2017, suggesting that in-state
sources of precursor emissions may not
be changing much, and may not be a big
factor potentially contributing to future
transport problems.6 We reiterate that
in-state monitored ozone levels were
just one piece of information that
helped to inform the EPA’s analysis and
conclusion.
Comment 4: The commenter said we
failed to mention that Alaska was not
included in the EPA’s modeling and
suggested the EPA may have considered
Alaska as an international contributor.
The commenter concluded that we
ignored Alaska emissions in our
modeling and for that reason it is not
appropriate to use the EPA’s modeling
data to identify downwind receptors in
the first step of our analysis.
Response 4: We disagree that the
proposal failed to explain the scope of
the modeling. Our proposal clearly
stated that the EPA conducted modeling
and released the data to states in the
form of several memoranda, but that
‘‘none [of the memoranda] project[ed]
design values at monitoring sites located
in Alaska, nor apportion[ed] specific
downwind impacts to Alaska.’’ 7 We
also stated that the memorandum
released in March of 2018 helped to
identify potential downwind receptors
in the first step of our analysis, but that
it did not inform whether Alaska was
sufficiently linked to those receptors,
under the second step of EPA’s four-step
analysis.8
Our proposal described the EPA’s
modeling domain (which included the
48 contiguous United States and the
District of Columbia) and referenced the
2018 memorandum, placed in the
docket for this action.9 The EPA did not
consider Alaska as an international
contributor to downwind states, nor did
we ignore Alaska emissions. Any
pollutant concentrations from Alaska
6 Proposal published June 5, 2019, 84 FR 26041;
at page 26045, Table 2.
7 Proposal published June 5, 2019, 84 FR 26041;
at page 26042, column 3.
8 Ibid. at page 26044, column 3.
9 Ibid. at page 26043, column 2.
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emissions would have been included as
part of the boundary condition
concentrations used as inputs to the
model. These boundary conditions
along the perimeter of our modeling
domain were derived from simulations
of the GEOSChem global chemistry
model for the year 2011.10 A description
of the GEOSChem modeling platform
leveraged for these boundary conditions
has been placed in the docket for this
action.11 We continue to believe it is
appropriate to use the modeling data
released in the EPA’s March 2018
memorandum to identify potential
downwind receptors at the first step in
our analysis.
Comment 5: The commenter claimed
that the EPA erred in calculating and
using geographic distance and the
relative emissions of intervening states
as factors in our analysis. The
commenter argued that it would be hard
to imagine other states making this kind
of assertion and the EPA treating it as
a valid approach.
Response 5: We believe it is
appropriate and reasonable to consider
the approximately 1,000-mile distance
from Alaska’s southernmost border to
the nearest identified nonattainment
and maintenance receptors (located in
Sacramento, California) as part of our
weight of evidence analysis in this
action. We also believe it is appropriate
to compare Alaska’s emissions to those
of intervening states (Washington and
Oregon), which are closer to the
Sacramento, California nonattainment
and maintenance receptors, and which
are not linked by the EPA’s modeling to
those Sacramento receptors. Our weight
of evidence analytical approach is
specific to Alaska and the submission
before us, and functions, in the absence
of the contribution data available with
respect to impacts on downwind states
within our modeling domain, to provide
a screening level of analysis that
Alaska’s emissions are not significantly
contributing to a downwind air quality
problem.12 Our evaluation considers not
just that the intervening states have
higher emissions, but that at those
higher levels, the impact on downwind
air quality problems does not exceed the
1% air quality threshold. Thus, it is
reasonable for the EPA to conclude that
10 The modeling domain is the area within the
purple rectangle in Figure 2–1 of the EPA’s Air
Quality Modeling Technical Support Document for
the Updated 2023 Projected Ozone Design Values,
dated December 2018.
11 B.H. Henderson et al.: A database and tool for
boundary conditions for regional air quality
modeling: Description and evaluation, Geosci.
Model Dev., 7, 339–360, 2014 (published February
18, 2014).
12 Proposal published June 5, 2019, 84 FR 26041;
at page 26045.
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Alaska, at a greater distance and with
lower emission levels, will also not
exceed that threshold. The EPA has in
fact employed this rationale in other
actions under the good neighbor
provision, where contribution modeling
data was unavailable.13
Comment 6: The commenter said the
EPA should not point to the Alaska SIPapproved major new source review
permitting programs as programs that
help address potential future interstate
transport of pollutants. The commenter
claimed no such program has ever
prevented a source from being
constructed due to interstate transport
concerns. The commenter further
claimed that state permitting officials
routinely ‘‘look the other way’’ and that
source owners and operators try to find
loopholes or restrict their modeling to
avoid performing analyses which would
show impacts to nearby states.
Response 6: In our proposal, we
pointed to Alaska’s SIP-approved
preconstruction permitting programs
(known as ‘‘new source review’’) as one
piece of evidence in our weight of
evidence analysis. We believe it is
appropriate for the EPA to evaluate the
current Federally-approved Alaska SIP
on its face for measures that control
emissions of ozone precursors. Alaska’s
new source review permitting programs
are Federally-enforceable measures
designed to control emissions from
proposed new and modified stationary
sources of regulated air pollutants,
including NOX and VOCs as precursors
to ozone.
We most recently approved revisions
to Alaska’s new source review
permitting programs on August 29, 2019
(84 FR 45419). Alaska routinely
evaluates new source review permit
applications from subject sources in
Alaska and issues permits containing
emission limits, work practice
standards, monitoring requirements and
other controls designed to ensure
compliance with emission limits and
provide for continued attainment of the
ozone NAAQS. The EPA cited this
program as helping to ensure that future
changes in emissions from Alaska are
not likely to lead to impermissible
impacts on air quality in downwind
states. Nonetheless, because the EPA
finds in this action that Alaska will not
significantly contribute to
nonattainment or interfere with
maintenance of the 2015 ozone NAAQS
downwind based on current emission
levels, Alaska does not have an
13 See prior interstate transport actions with
respect to the 2012 fine particulate matter NAAQS.
For example, the September 11, 2019 action on the
Utah SIP (84 FR 47893) and the August 20, 2018
action on the Washington SIP (83 FR 42031).
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69333
obligation to prohibit any specific level
of emissions in the State under the good
neighbor provision. Other provisions of
the CAA (e.g., sections 110(k)(5) and
126(b)) provide bases for reevaluating
this conclusion if future changes in
emissions change Alaska’s impact on
downwind states.
With respect to the commenter’s
concerns about implementation of
permitting programs, the comment is
vague and lacks supporting evidence or
documentation. Moreover, this
comment is related to implementation
of the SIP, and is therefore outside the
scope of this action. In the context of
acting on infrastructure and interstate
transport submissions, the EPA
evaluates the submitting state’s SIP for
facial compliance with statutory and
regulatory requirements, not for the
state’s implementation of its SIP.14 The
EPA has other authority to address any
issues concerning a state’s
implementation of the rules,
regulations, consent orders, etc. that
comprise its SIP.
Comment 7: The commenter asserted
the EPA should perform modeling and
affirmatively determine whether Alaska
sources significantly contribute to
nonattainment of the 2015 ozone
NAAQS in any other state or interfere
with maintenance of the 2015 ozone
NAAQS in any other state.
Response 7: To help states develop
interstate transport SIPs for the 2015
ozone NAAQS, the EPA modeled the
contiguous United States and the
District of Columbia and produced data
projecting future design values at
monitoring sites and apportioning
specific downwind impacts to upwind
states.15 The EPA’s modeling did not
quantify Alaska’s contribution to
downwind receptors, however nothing
in the CAA requires the EPA to do so
where other reasonable means are
available for evaluating Alaska’ s impact
to downwind receptors. The EPA did
not include Alaska in the modeling
domain primarily because it is remote
and isolated in relation to other states
with identified nonattainment and/or
maintenance receptors for the 2015
ozone NAAQS.
The EPA relied on the best
information available to inform its
decision and evaluated Alaska’s SIP
submission through a weight of
evidence analysis of information,
including emissions inventory data,
monitoring trends, geography,
meteorology, and SIP-approved
14 See U.S. Court of Appeals for the Ninth Circuit
decision in Montana Environmental Information
Center v. EPA, No. 16–71933 (Aug. 30, 2018).
15 See supra note 9.
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provisions that limit current and future
emissions of ozone precursors. The EPA
has used a weight of evidence analysis
to assess Alaska interstate transport SIP
submissions in the past, most recently
on June 27, 2018 (83 FR 30048).16 None
of the comments justify altering our
proposed approval of Alaska’s interstate
transport SIP submission for the 2015
ozone NAAQS. Therefore, we are
finalizing our action as proposed.
III. Final Action
We approve the Alaska SIP as meeting
CAA section 110(a)(2)(D)(i)(I)
requirements for the 2015 ozone
NAAQS. This action is being taken
under section 110 of the CAA.
IV. Statutory and Executive Order
Review
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);
• Is not an Executive Order 13771 (82
FR 9339, February 2, 2017) regulatory
action because SIP approvals are
exempted under Executive Order 12866;
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
action approved the Alaska SIP for
purposes of CAA section 110(a)(2)(D)(i)(I) with
respect to the 2012 fine particulate matter NAAQS.
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16 This
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• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide the EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
The SIP is not approved to apply on
any Indian reservation land or in any
other area where the EPA or an Indian
tribe has demonstrated that a tribe has
jurisdiction. In those areas of Indian
country, the rule does not have tribal
implications and it will not impose
substantial direct costs on tribal
governments or preempt tribal law as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000).
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing this action
and other required information to the
U.S. Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. A major rule cannot take effect
until 60 days after it is published in the
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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 CAA,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the appropriate
circuit by February 18, 2020. 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.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 2, 2019.
Chris Hladick,
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, amend the table in
paragraph (e) by adding the entry
‘‘Interstate Transport Requirements—
2015 Ozone NAAQS’’ at the end of the
table to read as follows:
■
§ 52.70
*
Identification of plan.
*
*
(e) * * *
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Federal Register / Vol. 84, No. 243 / Wednesday, December 18, 2019 / Rules and Regulations
69335
EPA-APPROVED ALASKA NONREGULATORY PROVISIONS AND QUASI-REGULATORY MEASURES
Name of SIP provision
Applicable
geographic or
nonattainment
area
State
submittal
date
*
*
*
Interstate Transport RequireStatewide ............ 10/25/2018
ments—2015 Ozone
NAAQS.
[FR Doc. 2019–27162 Filed 12–17–19; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 80
[EPA–HQ–OAR–2018–0638; FRL–10003–29–
OAR]
RIN 2060–AU74
Amendments Related to Global Marine
Fuel
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is amending its diesel
fuel regulations to allow fuel suppliers
to distribute distillate diesel fuel that
complies with the sulfur standard that
SUMMARY:
*
*
12/18/2019, [Insert Federal
Register citation].
NAICS code a
Industry ............................................................................
khammond on DSKJM1Z7X2PROD with RULES
Explanations
applies internationally for ships instead
of the fuel standards that otherwise
apply to distillate diesel fuel in the
United States. The affected fuel may not
be used in the United States’ Emission
Control Areas.
DATES: This final rule is effective on
December 18, 2019.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2018–0638. All
documents in the docket are listed on
the www.regulations.gov website.
Although listed in the index, some
information is not publicly available,
e.g., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically in
www.regulations.gov or in hard copy at
Category
a North
EPA approval date
*
*
Approves SIP for purposes of CAA section
110(a)(2)(D)(i)(I) for the 2015 Ozone
NAAQS.
Air and Radiation Docket and
Information Center, EPA Docket Center,
EPA/DC, EPA WJC West Building, 1301
Constitution Ave. NW, Room 3334,
Washington, DC. 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 Air Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT:
Robert Anderson, Office of
Transportation and Air Quality,
Environmental Protection Agency, (734)
214–4280; anderson.robert@epa.gov.
SUPPLEMENTARY INFORMATION:
A. Does this action apply to me?
This action relates to companies that
produce and distribute distillate diesel
fuel. Categories and entities that might
be affected include the following:
Examples of potentially affected entities
324110
424710
493190
Petroleum refineries (including importers).
Petroleum bulk stations and terminals.
Other warehousing and storage-bulk petroleum storage.
American Industry Classification System (NAICS).
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely
covered by these rules. This table lists
the types of entities that we are aware
may be regulated by this action. Other
types of entities not listed in the table
could also be regulated. To determine
whether your activities are regulated by
this action, you should carefully
examine the applicability criteria in the
referenced regulations. You may direct
questions regarding the applicability of
this action to the persons listed in the
preceding FOR FURTHER INFORMATION
CONTACT section.
B. What is the Agency’s authority for
taking this action?
EPA adopted sulfur standards for
marine diesel fuel under Clean Air Act
authority (42 U.S.C. 7401–7671q). The
VerDate Sep<11>2014
15:51 Dec 17, 2019
Jkt 250001
amendments in this rule are covered by
that same authority.
C. What is the effective date of this
action?
Section 553(d)(1) of the
Administrative Procedure Act, 5 U.S.C.
553(d)(1), provides that final rules shall
not become effective until 30 days after
publication in the Federal Register
‘‘except . . . a substantive rule which
grants or recognizes an exemption or
relieves a restriction.’’ The purpose of
this provision is to ‘‘give affected parties
a reasonable time to adjust their
behavior before the final rule takes
effect.’’ Omnipoint Corp. v. Fed.
Commc’n Comm’n, 78 F.3d 620, 630
(D.C. Cir. 1996); see also United States
v. Gavrilovic, 551 F.2d 1099, 1104 (8th
Cir. 1977) (quoting legislative history).
However, when the agency grants or
PO 00000
Frm 00041
Fmt 4700
Sfmt 4700
recognizes an exemption or relieves a
restriction, affected parties do not need
a reasonable time to adjust because the
effect is not adverse. EPA is issuing this
final rule under Clean Air Act section
307(d), which states ‘‘The provisions of
section 553 through 557. . . of Title 5
shall not, except as expressly provided
in this section, apply to actions to
which this subsection applies.’’ 42
U.S.C. 7607(d)(1). Thus, section 553(d)
of the Administrative Procedures Act
does not apply to this rule. EPA is
nevertheless acting consistently with
the policies underlying APA section
553(d) in making the regulations
contained in this final rule effective
upon publication in the Federal
Register. The regulatory amendments to
40 CFR part 80, subpart I, conditionally
exempt distillate marine diesel fuel
from the prohibition against distributing
E:\FR\FM\18DER1.SGM
18DER1
Agencies
[Federal Register Volume 84, Number 243 (Wednesday, December 18, 2019)]
[Rules and Regulations]
[Pages 69331-69335]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-27162]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R10-OAR-2018-0823; FRL-10003-24-Region 10]
Air Plan Approval; AK: Interstate Transport Requirements for the
2015 Ozone Standard
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: The Clean Air Act requires each State Implementation Plan
(SIP) to contain adequate provisions prohibiting emissions that will
have certain adverse air quality effects in other states. On October
25, 2018, the State of Alaska made a submission to the Environmental
Protection Agency (EPA) to address these requirements for the 2015
ozone National Ambient Air Quality Standards (NAAQS). The EPA approves
the Alaska SIP as meeting the requirement that each SIP contain
adequate provisions to prohibit emissions that will significantly
contribute to nonattainment or interfere with maintenance of the 2015
ozone NAAQS in any other state.
DATES: This final rule is effective January 17, 2020.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-R10-OAR-2018-0823. All documents in the docket are
listed on the https://www.regulations.gov website. Although listed in
the index, some information is not publicly available, e.g.,
Confidential Business Information or other information the disclosure
of which is restricted by statute. Certain other material, such as
copyrighted material, is not placed on the internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available at https://www.regulations.gov, or please
contact the person listed in the FOR FURTHER INFORMATION CONTACT
section for additional availability information.
FOR FURTHER INFORMATION CONTACT: Kristin Hall (15-H13), Air and
Radiation Division, EPA Region 10, 1200 Sixth Avenue (Suite 155),
Seattle, WA 98101, (206) 553-6357, [email protected].
SUPPLEMENTARY INFORMATION: Throughout this document wherever ``we,''
``us,'' or ``our'' is used, it refers to the EPA.
Table of Contents
I. Background
II. Response to Comment
III. Final Action
IV. Statutory and Executive Order Review
I. Background
On October 25, 2018, the Alaska Department of Environmental
Conservation (ADEC) made a submission addressing the interstate
transport requirements of CAA section 110(a)(2)(D)(i)(I) for the 2015
ozone NAAQS.\1\ This ``good neighbor'' provision of the CAA requires
that a SIP for a new or revised NAAQS must contain adequate provisions
prohibiting any source or other type of emissions activity within the
State from emitting air pollutants in amounts that will significantly
contribute to nonattainment of such NAAQS in any other state or that
will interfere with maintenance of the NAAQS in any other state.
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\1\ Alaska's October 25, 2018 submission addresses all CAA
sections 110(a)(1) and (2) infrastructure requirements for the 2015
ozone NAAQS (including interstate transport prongs 1 and 2) and
includes regulatory updates and permitting rule revisions for
approval into the SIP. This action addresses the portion of the
submission related to interstate transport prongs 1 and 2. We are
addressing the remainder of the submission in separate actions on
August 29, 2019 (84 FR 45419) and October 15, 2019 (84 FR 55094).
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On June 5, 2019, we proposed to approve Alaska's SIP submission (84
FR 26041). The reasons for our proposed approval are included in the
proposed
[[Page 69332]]
action and will not be restated here. The public comment period for the
proposed action closed on July 5, 2019. We received adverse comments
from one anonymous commenter. Following is our response to each
distinct issue raised by the commenter.
II. Response to Comment
Comment 1: The commenter stated that the EPA should not approve
Alaska's SIP submission because ADEC did not model Alaska emissions and
the effect of those emissions on other states and Canada.
Response 1: The commenter is correct that ADEC did not model Alaska
emissions and the effect of those emission on other states and Canada.
However, that is not a basis for disapproval in this instance. Alaska's
SIP submission included information and analysis on the amount and
sources of ozone precursor emissions from Alaska, trends in monitored
ambient ozone levels, meteorological conditions, distances from Alaska
to the nearest receptors in other states, and intervening geography
that isolates Alaska from other areas that have ozone problems. ADEC
concluded that emissions from Alaska sources do not significantly
contribute to nonattainment of the 2015 ozone NAAQS in any other state
and do not interfere with maintenance of the 2015 ozone NAAQS in any
other state.
In our review, we evaluated Alaska's SIP submission and conducted
our own weight of evidence analysis to determine whether we agreed with
ADEC's conclusion. We assessed emissions inventory data, monitoring
trends, geography, meteorology, and current SIP-approved provisions. We
found these factors sufficiently informative regarding Alaska's
potential to adversely impact air quality in downwind states without
conducting modeling of emissions as suggested by the commenter, and
therefore, proposed to approve the SIP submission. We note this is not
a new approach. The EPA has conducted weight of evidence analyses to
evaluate prior Alaska interstate transport SIP submissions, and we
believe it to be a reasonable and appropriate approach in this
instance.\2\
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\2\ Most recently, we took this approach in our June 27, 2018
action approving the Alaska SIP for purposes of CAA section
110(a)(2)(D)(i)(I) with respect to the 2012 fine particulate matter
NAAQS (83 FR 30048).
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The EPA further agrees that ADEC did not analyze potential
transport to Canada, but that is not a deficiency in the State's
analysis. The evaluation of international air quality impacts is not a
requirement under CAA section 110(a)(2)(D)(i)(I), which is the only
provision of the statute addressed in this action.\3\
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\3\ CAA sections 110(a)(2)(D)(ii) and 115 address international
pollution abatement. We proposed approval of this element for the
2015 ozone NAAQS in a separate action on October 15, 2019 (84 FR
55094). Alaska has no pending obligations under CAA section 115 with
respect to Canada or any other foreign country.
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Comment 2: The commenter stated, ``the EPA can't rely on relative
emissions to justify [a finding of] no significant contribution or
interference with maintenance'' of the 2015 ozone NAAQS. The commenter
also noted that, in our proposal, we showed that nitrogen oxide
(NOX) emissions from certain Alaska sources ranked second
highest in the region.
Response 2: The commenter is correct that, based on the 2014
National Emissions Inventory (2014 NEI), NOX emissions from
mobile and stationary sources in Alaska ranked second highest of the
Region 10 states.\4\ Our analysis, however, also compared Alaska
emissions to those nationwide and determined that, based on the 2014
NEI, NOX emissions from Alaska mobile and stationary sources
totaled just one percent of national NOX emissions.\5\ This
comparison of relative emissions puts Alaska emissions estimates into
context and is a useful exercise in evaluating the Alaska ozone
interstate transport SIP submission. Importantly, this was just one
factor in our weight of evidence analysis and was considered in
conjunction with other factors including monitoring trends, geography,
meteorology, and current SIP-approved provisions. In particular, the
fact that other, geographically-closer states with comparable or
greater emission levels did not impermissibly impact downwind air
quality problems supports the conclusion that Alaska emissions are not
likely to be linked to identified nonattainment and maintenance
receptors in any other state with respect to the 2015 ozone NAAQS. We
continue to find this to be true.
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\4\ Alaska's stationary and mobile source NOX
emissions were estimated to be 127,194 tons. Washington's emissions
were higher (234,050 tons), while Oregon and Idaho's emissions are
somewhat lower (125,626 and 81,135 tons, respectively).
\5\ Based on the 2014 NEI.
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Comment 3: The commenter took issue with the EPA's evaluation of
in-state monitored ozone levels. The commenter asserted that in-state
levels are not predictive of downwind levels.
Response 3: We found it informative to review in-state monitored
ozone levels as part of our weight of evidence analysis. This kind of
information can shed light on whether in-state conditions are changing
and whether those changes could have downwind implications. For
example, if ozone levels at monitoring sites in Alaska were rising over
time, it could suggest increased precursor emissions from Alaska
sources which could also have impacts on downwind air quality in other
states. In our proposal, we assessed monitored ozone trends in Alaska
and determined that in-state ozone levels were well below the 2015
ozone NAAQS. The table of design values in our proposal illustrated
that trends have been generally flat from 2010 to 2017, suggesting that
in-state sources of precursor emissions may not be changing much, and
may not be a big factor potentially contributing to future transport
problems.\6\ We reiterate that in-state monitored ozone levels were
just one piece of information that helped to inform the EPA's analysis
and conclusion.
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\6\ Proposal published June 5, 2019, 84 FR 26041; at page 26045,
Table 2.
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Comment 4: The commenter said we failed to mention that Alaska was
not included in the EPA's modeling and suggested the EPA may have
considered Alaska as an international contributor. The commenter
concluded that we ignored Alaska emissions in our modeling and for that
reason it is not appropriate to use the EPA's modeling data to identify
downwind receptors in the first step of our analysis.
Response 4: We disagree that the proposal failed to explain the
scope of the modeling. Our proposal clearly stated that the EPA
conducted modeling and released the data to states in the form of
several memoranda, but that ``none [of the memoranda] project[ed]
design values at monitoring sites located in Alaska, nor apportion[ed]
specific downwind impacts to Alaska.'' \7\ We also stated that the
memorandum released in March of 2018 helped to identify potential
downwind receptors in the first step of our analysis, but that it did
not inform whether Alaska was sufficiently linked to those receptors,
under the second step of EPA's four-step analysis.\8\
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\7\ Proposal published June 5, 2019, 84 FR 26041; at page 26042,
column 3.
\8\ Ibid. at page 26044, column 3.
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Our proposal described the EPA's modeling domain (which included
the 48 contiguous United States and the District of Columbia) and
referenced the 2018 memorandum, placed in the docket for this
action.\9\ The EPA did not consider Alaska as an international
contributor to downwind states, nor did we ignore Alaska emissions. Any
pollutant concentrations from Alaska
[[Page 69333]]
emissions would have been included as part of the boundary condition
concentrations used as inputs to the model. These boundary conditions
along the perimeter of our modeling domain were derived from
simulations of the GEOSChem global chemistry model for the year
2011.\10\ A description of the GEOSChem modeling platform leveraged for
these boundary conditions has been placed in the docket for this
action.\11\ We continue to believe it is appropriate to use the
modeling data released in the EPA's March 2018 memorandum to identify
potential downwind receptors at the first step in our analysis.
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\9\ Ibid. at page 26043, column 2.
\10\ The modeling domain is the area within the purple rectangle
in Figure 2-1 of the EPA's Air Quality Modeling Technical Support
Document for the Updated 2023 Projected Ozone Design Values, dated
December 2018.
\11\ B.H. Henderson et al.: A database and tool for boundary
conditions for regional air quality modeling: Description and
evaluation, Geosci. Model Dev., 7, 339-360, 2014 (published February
18, 2014).
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Comment 5: The commenter claimed that the EPA erred in calculating
and using geographic distance and the relative emissions of intervening
states as factors in our analysis. The commenter argued that it would
be hard to imagine other states making this kind of assertion and the
EPA treating it as a valid approach.
Response 5: We believe it is appropriate and reasonable to consider
the approximately 1,000-mile distance from Alaska's southernmost border
to the nearest identified nonattainment and maintenance receptors
(located in Sacramento, California) as part of our weight of evidence
analysis in this action. We also believe it is appropriate to compare
Alaska's emissions to those of intervening states (Washington and
Oregon), which are closer to the Sacramento, California nonattainment
and maintenance receptors, and which are not linked by the EPA's
modeling to those Sacramento receptors. Our weight of evidence
analytical approach is specific to Alaska and the submission before us,
and functions, in the absence of the contribution data available with
respect to impacts on downwind states within our modeling domain, to
provide a screening level of analysis that Alaska's emissions are not
significantly contributing to a downwind air quality problem.\12\ Our
evaluation considers not just that the intervening states have higher
emissions, but that at those higher levels, the impact on downwind air
quality problems does not exceed the 1% air quality threshold. Thus, it
is reasonable for the EPA to conclude that Alaska, at a greater
distance and with lower emission levels, will also not exceed that
threshold. The EPA has in fact employed this rationale in other actions
under the good neighbor provision, where contribution modeling data was
unavailable.\13\
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\12\ Proposal published June 5, 2019, 84 FR 26041; at page
26045.
\13\ See prior interstate transport actions with respect to the
2012 fine particulate matter NAAQS. For example, the September 11,
2019 action on the Utah SIP (84 FR 47893) and the August 20, 2018
action on the Washington SIP (83 FR 42031).
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Comment 6: The commenter said the EPA should not point to the
Alaska SIP-approved major new source review permitting programs as
programs that help address potential future interstate transport of
pollutants. The commenter claimed no such program has ever prevented a
source from being constructed due to interstate transport concerns. The
commenter further claimed that state permitting officials routinely
``look the other way'' and that source owners and operators try to find
loopholes or restrict their modeling to avoid performing analyses which
would show impacts to nearby states.
Response 6: In our proposal, we pointed to Alaska's SIP-approved
preconstruction permitting programs (known as ``new source review'') as
one piece of evidence in our weight of evidence analysis. We believe it
is appropriate for the EPA to evaluate the current Federally-approved
Alaska SIP on its face for measures that control emissions of ozone
precursors. Alaska's new source review permitting programs are
Federally-enforceable measures designed to control emissions from
proposed new and modified stationary sources of regulated air
pollutants, including NOX and VOCs as precursors to ozone.
We most recently approved revisions to Alaska's new source review
permitting programs on August 29, 2019 (84 FR 45419). Alaska routinely
evaluates new source review permit applications from subject sources in
Alaska and issues permits containing emission limits, work practice
standards, monitoring requirements and other controls designed to
ensure compliance with emission limits and provide for continued
attainment of the ozone NAAQS. The EPA cited this program as helping to
ensure that future changes in emissions from Alaska are not likely to
lead to impermissible impacts on air quality in downwind states.
Nonetheless, because the EPA finds in this action that Alaska will not
significantly contribute to nonattainment or interfere with maintenance
of the 2015 ozone NAAQS downwind based on current emission levels,
Alaska does not have an obligation to prohibit any specific level of
emissions in the State under the good neighbor provision. Other
provisions of the CAA (e.g., sections 110(k)(5) and 126(b)) provide
bases for reevaluating this conclusion if future changes in emissions
change Alaska's impact on downwind states.
With respect to the commenter's concerns about implementation of
permitting programs, the comment is vague and lacks supporting evidence
or documentation. Moreover, this comment is related to implementation
of the SIP, and is therefore outside the scope of this action. In the
context of acting on infrastructure and interstate transport
submissions, the EPA evaluates the submitting state's SIP for facial
compliance with statutory and regulatory requirements, not for the
state's implementation of its SIP.\14\ The EPA has other authority to
address any issues concerning a state's implementation of the rules,
regulations, consent orders, etc. that comprise its SIP.
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\14\ See U.S. Court of Appeals for the Ninth Circuit decision in
Montana Environmental Information Center v. EPA, No. 16-71933 (Aug.
30, 2018).
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Comment 7: The commenter asserted the EPA should perform modeling
and affirmatively determine whether Alaska sources significantly
contribute to nonattainment of the 2015 ozone NAAQS in any other state
or interfere with maintenance of the 2015 ozone NAAQS in any other
state.
Response 7: To help states develop interstate transport SIPs for
the 2015 ozone NAAQS, the EPA modeled the contiguous United States and
the District of Columbia and produced data projecting future design
values at monitoring sites and apportioning specific downwind impacts
to upwind states.\15\ The EPA's modeling did not quantify Alaska's
contribution to downwind receptors, however nothing in the CAA requires
the EPA to do so where other reasonable means are available for
evaluating Alaska' s impact to downwind receptors. The EPA did not
include Alaska in the modeling domain primarily because it is remote
and isolated in relation to other states with identified nonattainment
and/or maintenance receptors for the 2015 ozone NAAQS.
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\15\ See supra note 9.
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The EPA relied on the best information available to inform its
decision and evaluated Alaska's SIP submission through a weight of
evidence analysis of information, including emissions inventory data,
monitoring trends, geography, meteorology, and SIP-approved
[[Page 69334]]
provisions that limit current and future emissions of ozone precursors.
The EPA has used a weight of evidence analysis to assess Alaska
interstate transport SIP submissions in the past, most recently on June
27, 2018 (83 FR 30048).\16\ None of the comments justify altering our
proposed approval of Alaska's interstate transport SIP submission for
the 2015 ozone NAAQS. Therefore, we are finalizing our action as
proposed.
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\16\ This action approved the Alaska SIP for purposes of CAA
section 110(a)(2)(D)(i)(I) with respect to the 2012 fine particulate
matter NAAQS.
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III. Final Action
We approve the Alaska SIP as meeting CAA section 110(a)(2)(D)(i)(I)
requirements for the 2015 ozone NAAQS. This action is being taken under
section 110 of the CAA.
IV. Statutory and Executive Order Review
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);
Is not an Executive Order 13771 (82 FR 9339, February 2,
2017) regulatory action because SIP approvals are exempted under
Executive Order 12866;
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
Does not have federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of Section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Does not provide the EPA with the discretionary authority
to address, as appropriate, disproportionate human health or
environmental effects, using practicable and legally permissible
methods, under Executive Order 12898 (59 FR 7629, February 16, 1994).
The SIP is not approved to apply on any Indian reservation land or
in any other area where the EPA or an Indian tribe has demonstrated
that a tribe has jurisdiction. In those areas of Indian country, the
rule does not have tribal implications and it will not impose
substantial direct costs on tribal governments or preempt tribal law as
specified by Executive Order 13175 (65 FR 67249, November 9, 2000).
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. The EPA will submit a report containing this action and
other required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A major rule cannot
take effect until 60 days after it is published in the Federal
Register. This action is not a ``major rule'' as defined by 5 U.S.C.
804(2).
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by February 18, 2020. 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.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 2, 2019.
Chris Hladick,
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, amend the table in paragraph (e) by adding the entry
``Interstate Transport Requirements--2015 Ozone NAAQS'' at the end of
the table to read as follows:
Sec. 52.70 Identification of plan.
* * * * *
(e) * * *
[[Page 69335]]
EPA-Approved Alaska Nonregulatory Provisions and Quasi-Regulatory Measures
----------------------------------------------------------------------------------------------------------------
State
Name of SIP provision Applicable geographic or submittal EPA approval date Explanations
nonattainment area date
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* * * * * * *
Interstate Transport Statewide................ 10/25/2018 12/18/2019, [Insert Approves SIP for
Requirements--2015 Ozone NAAQS. Federal Register purposes of CAA
citation]. section
110(a)(2)(D)(i)(I
) for the 2015
Ozone NAAQS.
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[FR Doc. 2019-27162 Filed 12-17-19; 8:45 am]
BILLING CODE 6560-50-P