Air Plan Approval; Florida; 2008 8-Hour Ozone Interstate Transport, 4403-4407 [2019-02542]
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Federal Register / Vol. 84, No. 32 / Friday, February 15, 2019 / Proposed Rules
5. Amend § 2.22 by:
a. Removing the word ‘‘and’’ at the
end of paragraph (a)(19);
■ b. Removing the period at the end of
paragraph (a)(20) and adding ‘‘; and’’ in
its place; and
■ c. Adding paragraph (a)(21).
The addition reads as follows:
■
■
§ 2.22 Requirements for a TEAS Plus
application.
(a) * * *
(21) An applicant whose domicile or
principal place of business is not
located within the United States or its
territories must designate an attorney as
the applicant’s representative, pursuant
to § 2.11(a).
*
*
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■ 6. Amend § 2.32 by revising paragraph
(a)(4) to read as follows:
§ 2.32 Requirements for a complete
trademark or service mark application.
(a) * * *
(4) The address of the applicant.
When the applicant is, or must be,
represented by a practitioner, as defined
in § 11.1 of this chapter, who is
qualified to practice under § 11.14 of
this chapter, the practitioner’s name,
postal address, email address, and bar
information;
*
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PART 11—REPRESENTATION OF
OTHERS BEFORE THE UNITED
STATES PATENT AND TRADEMARK
OFFICE
7. The authority citation for 37 CFR
part 11 continues to read as follows:
■
Authority: 5 U.S.C. 500, 15 U.S.C. 1123,
35 U.S.C. 2(b)(2), 32, 41; Sec. 1, Pub. L. 113–
227, 128 Stat. 2114.
8. Amend § 11.14 by revising
paragraphs (c) and (e) to read as follows:
■
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(c) Foreigners. (1) Any foreign
attorney or agent not a resident of the
United States who shall file a written
application for reciprocal recognition
under paragraph (f) of this section and
prove to the satisfaction of the OED
Director that he or she is a registered
and active member in good standing
before the trademark office of the
country in which he or she resides and
practices and possesses good moral
character and reputation, may be
recognized for the limited purpose of
representing parties located in such
country before the Office in the
presentation and prosecution of
trademark matters, provided: The
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Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
provision of the Clean Air Act (CAA or
Act) for the 2008 8-hour ozone National
Ambient Air Quality Standards
(NAAQS). The good neighbor provision
requires each state’s implementation
plan to address the interstate transport
of air pollution in amounts that
contribute significantly to
nonattainment, or interfere with
maintenance of a NAAQS in any other
state. In this action, EPA is proposing to
determine that Florida’s SIP contains
adequate provisions to prohibit
emissions within the state from
contributing significantly to
nonattainment or interfering with
maintenance of the 2008 8-hour ozone
NAAQS in any other state.
DATES: Comments must be received on
or before March 18, 2019.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R04–
OAR–2018–0542 at https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Once submitted, comments cannot be
edited or removed from regulations.gov.
EPA may publish any comment received
to its public docket. Do not submit
electronically any information you
consider to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Multimedia submissions (audio, video,
etc.) must be accompanied by a written
comment. The written comment is
considered the official comment and
should include discussion of all points
you wish to make. EPA will generally
not consider comments or comment
contents located outside of the primary
submission (i.e., on the web, cloud, or
other file sharing system). For
additional submission methods, the full
EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www2.epa.gov/dockets/
commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT:
Nacosta C. Ward, Air Regulatory
Management Section, Air Planning and
Implementation Branch, Air, Pesticides
and Toxics Management Division, U.S.
Environmental Protection Agency,
Region 4, 61 Forsyth Street SW, Atlanta,
Georgia 30303–8960. Ms. Ward can also
be reached via telephone at (404) 562–
9140 and via electronic mail at
ward.nacosta@epa.gov.
SUPPLEMENTARY INFORMATION:
The Environmental Protection
Agency (EPA) is proposing to approve
Florida’s October 3, 2017, State
Implementation Plan (SIP) submission
pertaining to the ‘‘good neighbor’’
I. Background
On March 12, 2008, EPA promulgated
an ozone NAAQS that revised the levels
of the primary and secondary 8-hour
ozone standards from 0.08 parts per
Dated: February 6, 2019.
Andrei Iancu,
Under Secretary of Commerce for Intellectual
Property and Director of the United States
Patent and Trademark Office.
[FR Doc. 2019–02154 Filed 2–14–19; 8:45 am]
BILLING CODE 3510–16–P
§ 11.14 Individuals who may practice
before the Office in trademark and other
non-patent matters.
*
trademark office of such country and the
USPTO have reached an official
understanding to allow substantially
reciprocal privileges to those permitted
to practice in trademark matters before
the Office. Recognition under this
paragraph (c) shall continue only during
the period that the conditions specified
in this paragraph (c) obtain.
(2) In any trademark matter where a
foreign attorney or agent authorized
under paragraph (c)(1) of this section is
representing an applicant, registrant, or
party to a proceeding, an attorney, as
defined in § 11.1 and qualified to
practice under paragraph (a) of this
section, must also be appointed
pursuant to § 2.17(b) and (c) of this
chapter as the representative with
whom the Office will communicate and
conduct business.
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(e) Appearance. No individual other
than those specified in paragraphs (a),
(b), and (c) of this section will be
permitted to practice before the Office
in trademark matters on behalf of a
client. Except as specified in § 2.11(a) of
this chapter, an individual may appear
in a trademark or other non-patent
matter in his or her own behalf or on
behalf of:
(1) A firm of which he or she is a
member;
(2) A partnership of which he or she
is a partner; or
(3) A corporation or association of
which he or she is an officer and which
he or she is authorized to represent.
*
*
*
*
*
4403
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R04–OAR–2018–0542; FRL–9989–59–
Region 4]
Air Plan Approval; Florida; 2008 8-Hour
Ozone Interstate Transport
AGENCY:
SUMMARY:
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million (ppm) to 0.075 ppm.1 See 73 FR
16436 (March 27, 2008). Pursuant to
CAA section 110(a)(1), within three
years after promulgation of a new or
revised NAAQS (or shorter, if EPA
prescribes), states must submit SIPs that
meet the applicable requirements of
section 110(a)(2). EPA has historically
referred to these SIP submissions made
for the purpose of satisfying the
requirements of sections 110(a)(1) and
110(a)(2) as ‘‘infrastructure SIP’’
submissions. One of the structural
requirements of section 110(a)(2) is
section 110(a)(2)(D)(i), which generally
requires SIPs to contain adequate
provisions to prohibit in-state emissions
activities from having certain adverse
air quality effects on neighboring states
due to interstate transport of air
pollution. There are four sub-elements,
or ‘‘prongs,’’ within section
110(a)(2)(D)(i) of the CAA. CAA section
110(a)(2)(D)(i)(I), also known as the
‘‘good neighbor’’ provision, requires
SIPs to include provisions prohibiting
any source or other type of emissions
activity in one state from emitting any
air pollutant in amounts that will
contribute significantly to
nonattainment, or interfere with
maintenance, of the NAAQS in another
state. The two provisions of this section
are referred to as prong 1 (significant
contribution to nonattainment) and
prong 2 (interference with
maintenance). Section 110(a)(2)(D)(i)(II)
requires SIPs to contain adequate
provisions to prohibit emissions that
will interfere with measures required to
be included in the applicable
implementation plan for any other state
under part C to prevent significant
deterioration of air quality (prong 3) or
to protect visibility (prong 4). This
proposed action addresses only prongs
1 and 2 of section 110(a)(2)(D)(i). All
other infrastructure SIP elements for
Florida for the 2008 8-hour ozone
NAAQS were addressed in separate
rulemakings.2
A. State Submittal
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On October 3, 2017, the Florida
Department of Environmental Protection
(FDEP) provided a SIP submittal 3 to
EPA to address the interstate transport
requirements of sections
110(a)(2)(D)(i)(I) for the Florida SIP.
1 0.075
ppm equates to 75 parts per billion (ppb).
78 FR 65559 (November 1, 2013); 79 FR
50554 (August 25, 2014).
3 This submittal supplements an October 31, 2011
submittal addressing other infrastructure SIP
elements for Florida for the 2008 Ozone NAAQS.
See 78 FR 65559, 79 FR 50554. Although the
transmittal letter is dated October 3, 2017, EPA did
not receive Florida’s submittal until October 12,
2017.
2 See
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Florida made this submission to certify
that its SIP contains adequate provisions
to prohibit emissions activities within
the State which will contribute
significantly to nonattainment or
interfere with maintenance of the 2008
8-hour ozone NAAQS in any other state,
and therefore, adequately addresses the
requirements of CAA section
110(a)(2)(D)(i)(I) for the 2008 8-hour
ozone NAAQS.4 Florida’s certification is
based on emissions generating activities,
air quality monitoring and modeling
data, and SIP-approved and state
provisions regulating emissions of
ozone precursors (volatile organic
compounds (VOCs) and nitrogen oxides
(NOX)) within the State.
B. EPA’s Analysis Related to
110(a)(2)(D)(i)(I) for the 2008 8-Hour
Ozone NAAQS
EPA developed technical information
and related analyses to assist states with
meeting section 110(a)(2)(D)(i)(I)
requirements for the 2008 8-hour ozone
NAAQS through SIPs and, as
appropriate, to provide backstop federal
implementation plans (FIPs) in the
event that states failed to submit
approvable SIPs.5 On October 26, 2016
(81 FR 74504), EPA took steps to
effectuate this backstop role with
respect to eastern states 6 by finalizing
an update to the Cross-State Air
Pollution Rule (CSAPR) ozone season
program that addresses good neighbor
obligations for the 2008 8-hour ozone
NAAQS (‘‘CSAPR Update’’). The CSAPR
Update establishes statewide NOX
budgets for certain affected electricity
generating units in 22 eastern states for
the May–September ozone season to
reduce the interstate transport of ozone
pollution in the eastern United States,
and thereby help downwind states and
communities meet and maintain the
4 On July 13, 2015, EPA published a final rule that
finalized findings of failure to submit with regard
to the requirements of CAA section 110(a)(2)(D)(i)(I)
for 24 states, including Florida, with respect to the
2008 ozone NAAQS. See 80 FR 39961. The findings
of failure to submit established a two-year deadline
for EPA to promulgate a FIP to address the
interstate transport SIP requirements pertaining to
significant contribution to nonattainment and
interference with maintenance unless, prior to EPA
promulgating a FIP, the state submits, and EPA
approves, a SIP that meets these requirements.
Additional background on the findings of failure to
submit—including Florida’s finding—can be found
in the preamble to the final rule findings.
5 The EPA issued a Notice of Data Availability on
August 4, 2015 requesting comment on the
modeling platform and air quality modeling results
that were used for the proposed CSAPR Update. See
80 FR 46271.
6 For purposes of the CSAPR Update, ‘‘eastern’’
states refer to all contiguous states fully east of the
Rocky Mountains (thus not including the mountain
states of Montana, Wyoming, Colorado, or New
Mexico).
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2008 8-hour ozone NAAQS. See 81 FR
74506. The rule also determined that
emissions from 14 states (including
Florida) will not significantly contribute
to nonattainment or interfere with
maintenance of the 2008 ozone NAAQS
in downwind states. Accordingly, EPA
determined that it need not require
further emission reductions from
sources in those states to address the
good neighbor provision as to the 2008
ozone NAAQS. Id.
The CSAPR Update used the same
framework that EPA used when
developing the original 2011 CSAPR,
EPA’s interstate transport rule
addressing the 1997 8-hour ozone
NAAQS as well as the 1997 and 2006
fine particulate matter (PM2.5) NAAQS.
The CSAPR framework establishes the
following four-step process to address
the requirements of the good neighbor
provision: (1) Identify downwind areas,
referred to as receptors, that are
expected to have problems attaining or
maintaining the NAAQS; (2) determine
which upwind states impact these
identified problems in amounts
sufficient to ‘‘link’’ them to the
downwind air quality problems; (3) for
states linked to downwind air quality
problems, identify upwind emissions, if
any, that will significantly contribute to
nonattainment or interfere with
maintenance of a NAAQS; and (4)
reduce the identified upwind emissions
for states that are found to have
emissions that will significantly
contribute to nonattainment or interfere
with maintenance of the NAAQS
downwind by adopting permanent and
enforceable measures in a FIP or SIP. In
the CSAPR Update, EPA used this fourstep framework to determine whether
states in the east will significantly
contribute to nonattainment or
interference with maintenance of
downwind air quality. As explained
below, the CSAPR Update’s four-step
analysis supports the conclusions
provided in FDEP’s October 3, 2017,
interstate transport SIP for the 2008 8hour ozone NAAQS that the State will
not significantly contribute to
nonattainment or interfere with
maintenance of the standard in other
states.
In the technical analysis supporting
the CSAPR Update, EPA used detailed
air quality analyses to determine where
projected nonattainment or maintenance
receptors would be, at step 1 of the fourstep framework, and whether emissions
from an eastern state contribute to
downwind air quality problems at those
projected nonattainment or maintenance
receptors, at step 2 of the framework.
Specifically, EPA determined whether
each state’s contributing emissions were
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at or above a specific threshold (i.e., one
percent of the ozone NAAQS). EPA
determined that one percent was an
appropriate threshold to use in this
analysis because there were important,
even if relatively small, contributions to
identified nonattainment and
maintenance receptors from multiple
upwind states at that threshold.7 See 81
FR 74504 (October 26, 2016). For the
CSAPR Update, EPA applied an air
quality screening threshold of 0.75 ppb
(one percent of the 2008 8-hour ozone
NAAQS of 75 ppb) to identify linkages
between upwind states and the
downwind nonattainment and
maintenance receptors. States with
impacts below the one-percent
threshold were considered not to
contribute to identified downwind
nonattainment and maintenance
receptors and therefore would not
contribute significantly to
nonattainment or interfere with
maintenance of the standard in those
downwind areas. If a state’s impact was
equal to or exceeded the one-percent
threshold, that state was considered
‘‘linked’’ to the downwind
nonattainment or maintenance
receptor(s) and the state’s emissions
were further evaluated, taking into
account both air quality and cost
considerations, to determine whether
any emissions reductions might be
necessary to address the state’s
obligation pursuant to CAA section
110(a)(2)(D)(i)(I).
As discussed in the final rule for the
CSAPR Update, the air quality modeling
contained in EPA’s technical analysis:
(1) Identified locations in the U.S.
where EPA anticipated nonattainment
or maintenance issues in 2017 for the
7 EPA’s analysis showed that the one-percent
threshold generally captured a high percentage of
the total pollution transport affecting downwind
states. EPA’s analysis further showed that the
application of a lower threshold would result in
relatively modest increases in the overall
percentage of ozone transport pollution captured,
while the use of higher thresholds would result in
a relatively large reduction in the overall percentage
of ozone pollution transport captured relative to the
levels captured at one percent at the majority of the
receptors. See 81 FR 74504 (October 26, 2016) and
‘‘Air Quality Modeling Final Rule Technical
Support Document for the Final CSAPR Update’’
(CSAPR Update Modeling TSD), available at https://
www.epa.gov/sites/production/files/2017-05/
documents/aq_modeling_tsd_final_csapr_
update.pdf. This approach is consistent with the
use of a one-percent threshold to identify those
states ‘‘linked’’ to air quality problems with respect
to the 1997 8-hour ozone NAAQS in the original
CSAPR rulemaking, wherein EPA noted that there
are adverse health impacts associated with ambient
ozone even at low levels. See 76 FR 48208 (August
8, 2011). See technical support document for the
August 8, 2011 final rule ‘‘Federal Implementation
Plans: Interstate Transport of Fine Particulate
Matter and Ozone and Correction of SIP’’
approvals’’ located at https://www.regulations.gov/
document?D=EPA-HQ-OAR-2009-0491-4140.
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2008 8-hour ozone NAAQS (these were
identified as nonattainment or
maintenance receptors, respectively),
and (2) quantified the projected
contributions from emissions from
upwind states to downwind ozone
concentrations at the receptors in 2017.
See 81 FR 74504 (October 26, 2016).
This modeling used the Comprehensive
Air Quality Model with Extensions
(CAMx version 6.11) to model the 2011
base year and the 2017 future base case
emissions scenarios to identify
projected nonattainment and
maintenance sites with respect to the
2008 8-hour ozone NAAQS in 2017.
EPA used nationwide state-level ozone
source apportionment modeling (the
CAMx Ozone Source Apportionment
Technology/Anthropogenic Precursor
Culpability Analysis technique) to
quantify the contribution of 2017 base
case NOX and VOC emissions from all
sources in each state to the 2017
projected receptors. The air quality
model runs were performed for a
modeling domain that covers the 48
contiguous United States, the District of
Columbia, and adjacent portions of
Canada and Mexico. The updated
modeling data released to support the
final CSAPR Update for Florida are the
most up-to-date information EPA has
developed to inform the Agency’s
analysis of upwind state linkages to
downwind air quality problems for the
2008 8-hour ozone NAAQS. See ‘‘Air
Quality Modeling Final Rule Technical
Support Document for the Final CSAPR
Update’’ (CSAPR Update Modeling
TSD).8
EPA’s air quality modeling for the
final CSAPR Update indicated that
Florida’s largest impact on any
projected downwind nonattainment
receptor in 2017 was 0.71 ppb, which is
below the one-percent threshold.
Accordingly, Florida is not ‘‘linked’’ to
any nonattainment receptors in EPA’s
modeling. Although the modeling for
the proposed CSAPR Update did not
link Florida’s emissions to any
maintenance receptors, the updated
modeling conducted for the final
CSAPR Update indicated that Florida’s
largest contribution to any projected
downwind maintenance-only site in
2017 would be 0.75 ppb.9 EPA’s
modeling indicated an average
8 See ‘‘Air Quality Modeling Final Rule Technical
Support Document for the Final CSAPR Update’’
(CSAPR Update Modeling TSD), available at https://
www.epa.gov/sites/production/files/2017-05/
documents/aq_modeling_tsd_final_csapr_
update.pdf.
9 See CSAPR Update Modeling TSD at Table 4–
2, section 4.4 and Appendix D located at available
at https://www.epa.gov/sites/production/files/201705/documents/aq_modeling_tsd_final_csapr_
update.pdf.
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contribution at the 0.75 ppb threshold to
the 2017 design values at two receptors
in Houston, Texas (i.e., Harris County
sites 482010024 and 482011034).
EPA received a comment on the
CSAPR Update proposal 10 stating that
the version of CAMx used for the
proposal modeling (CAMx v6.11) did
not include the most recent halogen
chemistry that would affect ozone
concentrations in saltwater marine
atmospheres and transport of ozone
from Florida to receptors in Texas. The
commenter stated that EPA should
include this chemistry in modeling for
the final rule. See 81 FR 74504 (October
26, 2016). A report by the CAMx model
developer on the impact of modeling
with the latest CAMx halogen chemistry
indicates that the updated chemistry
results in lower modeled ozone in air
transported over saltwater marine
environments for multiple days.11
Specifically, the report notes that on
days with multi-day transport across the
Gulf of Mexico, modeling with the
updated chemistry could lower 8-hour
daily maximum ozone concentrations
by up to 2 to 4 ppb in locations in
eastern Texas, including Houston. Air
parcel trajectories for individual days
used in EPA’s calculation of the
contribution from Florida to the
Houston receptors confirm that on days
with high modeled transport from
Florida to the receptors in Houston, air
travels for multiple days over the Gulf
of Mexico from Florida before reaching
the receptors in Houston.12 In the final
rule modeling, EPA was not able to
explicitly account for the updated
chemistry because this chemistry had
not yet been included by the model
developer in the source apportionment
tool in CAMx at the time the modeling
was performed for this rule. However,
because Florida’s maximum impact on
receptors in Houston, Texas, is exactly
10 See
80 FR 75706 (December 3, 2015).
Yarwood, G., T. Sakulyanontvittaya, O.
Nopmongcol, and B. Koo, 2014. Ozone Depletion by
Bromine and Iodine over the Gulf of Mexico Final
Report. Prepared for the Texas Commission on
Environmental Quality. November 2014. Ramboll
Environ International Corporation, Novato, CA and
Yarwood, G., J. Jung, O. Nopmongcol, and C. Emery,
2012. Improving CAMx Performance in Simulating
Ozone Transport from the Gulf of Mexico. Prepared
for the Texas Commission on Environmental
Quality. September 2012. Ramboll Environ
International Corporation, Novato, CA. These
studies are available in the docket for the CSAPR
Update Rule as EPA–HQ–OAR–2015–0500–0458
and EPA–HQ–OAR–2015–0500–0457, respectively.
12 More details and analysis of the impact of the
CAMx halogen chemistry updates on the
contributions from Florida and other Gulf Coast
states can be found in section 4.4 and Appendix D
to the CSAPR Update Modeling TSD available at
https://www.epa.gov/sites/production/files/201705/documents/aq_modeling_tsd_final_csapr_
update.pdf.
11 See
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at the 0.75 ppb threshold, the Agency
concluded that if it had performed the
final rule modeling with the updated
halogen chemistry, Florida’s impact
would likely be below this threshold.
Therefore, EPA determined in the
CSAPR Update that when this updated
halogen chemistry is considered, there
are no identified linkages between
Florida and 2017 downwind projected
nonattainment and maintenance
receptors. As a result of the modeling,
EPA did not finalize a FIP that required
NOX emission reductions from Florida
in the CSAPR Update because EPA’s
analysis performed to support the final
rule does not indicate that the State is
linked to any identified downwind
nonattainment or maintenance receptors
with respect to the 2008 8-hour ozone
NAAQS. Rather, in the CSAPR Update,
EPA took final action to determine that
emissions from Florida will not
significantly contribute to
nonattainment or interfere with
maintenance of the 2008 8-hour ozone
NAAQS in any other states.
Additionally, the CSAPR Update
addressed the decision from the United
States Court of Appeals for the District
of Columbia Circuit in EME Homer City
Generation, L.P. v. EPA, 795 F.3d 118
(D.C. Cir. 2015), remanding for
reconsideration certain states’ ozone
season NOX emission budgets from the
original CSAPR (including Florida’s)
with respect to the 1997 8-hour ozone
NAAQS.13 EPA removed Florida from
the CSAPR ozone season trading
program beginning in 2017.14
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II. What is EPA’s analysis of the Florida
submittal?
As mentioned in section I of this
document, Florida’s October 3, 2017
submittal certifies that emission
activities from the State will not
contribute significantly to
nonattainment or interfere with
maintenance of the 2008 8-hour ozone
13 Among other things, the decision remanded
CSAPR without vacatur for reconsideration of the
EPA’s emission budgets for certain states. The court
declared invalid the CSAPR Phase 2 NOX ozone
season emission budgets of 11 states, including
Florida, holding that those budgets over-control
with respect to the downwind air quality problems
to which those states were linked for the 1997
ozone NAAQS. Because the 2008 ozone NAAQS is
more stringent than the 1997 ozone NAAQS, the
CSAPR Update modeling necessarily indicates that
Florida is also not linked to any remaining air
quality concerns with respect to the 1997 ozone
standard for which the states were regulated in the
original CSAPR. For Florida, EPA therefore relieved
sources in the State from the obligation to comply
with the NOX ozone season trading program in
response to the remand. The court also remanded
without vacatur the CSAPR Phase 2 SO2 annual
emission budgets for four states (Alabama, Georgia,
South Carolina, and Texas) for reconsideration.
14 See 81 FR 74523–74524, October 26, 2016.
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NAAQS in any other state for the
following reasons: (1) Modeling
conducted by EPA in support of the
CSAPR Update indicates that Florida’s
impact on any downwind receptor is
less than one percent of the standard; (2)
NOX and VOC precursor emissions and
monitored ozone concentrations in
Florida have decreased since 2000; and
(3) Florida has SIP-approved stationary
source emissions standards and
monitoring and permitting regulations
in place addressing certain emissions
generating activities that contribute to
ozone precursor emissions. Based on an
assessment of this information, EPA
proposes to approve Florida’s SIP
submission because it has adequate
provisions to ensure that emissions from
sources within the State will not
significantly contribute to
nonattainment or interfere with
maintenance of the 2008 8-hour ozone
NAAQS in any other state.
Florida’s submittal assessed EPA’s
CSAPR Update modeling that showed
Florida’s contribution to downwind
receptors for the 2008 8-hour ozone
NAAQS is less than one percent of the
standard (i.e., 0.75 ppb), except as
follows. As discussed in Florida’s
October 3, 2017 SIP submission, the
CSAPR Update 2017 modeling
generated an average contribution from
Florida at the 0.75 ppb threshold to two
receptors in Houston, Texas (i.e., Harris
County sites 482010024 and
482011034). However, as discussed in
section I.B of this document and the
CSAPR Update, a newer version of the
CAMx chemical mechanism contains
updated chemical reactions (halogen
chemistry) which may have an impact
on the estimated ozone contributions
from Florida emissions to Houston
receptors. In the final rule modeling,
EPA was not able to explicitly account
for the updated chemistry because this
chemistry had not yet been included by
the model developer in the source
apportionment tool in CAMx at the time
the modeling was performed for this
final rule. However, because Florida’s
maximum contribution to receptors in
Houston, Texas is exactly at the 0.75
ppb threshold, the Agency believes that
if it had performed the final rule
modeling with the updated halogen
chemistry, Florida’s contribution would
likely be below the 0.75 ppb threshold.
Therefore, EPA concluded that Florida’s
emissions will not contribute to
downwind nonattainment and
maintenance receptors when
considering updated halogen chemistry
and therefore, did not finalize a FIP that
required NOX emission reductions from
Florida in the CSAPR Update.
PO 00000
Frm 00030
Fmt 4702
Sfmt 4702
Accordingly, in the CSAPR Update, EPA
already made a final determination that
Florida emissions will not significantly
contribute to nonattainment or interfere
with the 2008 ozone NAAQS in other
states and that sources in the State are
not required to further reduce emissions
pursuant to the good neighbor provision
with respect to this standard.
Florida’s submittal also notes that
total NOX and non-biogenic VOC
emissions in Florida have decreased by
52 percent and 44 percent, respectively,
since 2000. Florida indicates that
monitored ozone concentrations in the
State are also trending downward,
which correlates to the decline in ozone
precursor emissions.15
Florida also identified SIP-approved
regulations in the Florida
Administrative Code, including
Chapters 62–204, 62–210, and 62–212,
that provide for the implementation of
a permitting program required under
title I, parts C and D of the CAA for
sources of NOX and VOC ozone
precursors that contribute to ambient
ozone concentrations. The permitting
requirements help ensure that no new or
modified sources in the State subject to
these permitting regulations will
contribute significantly to
nonattainment or interfere with
maintenance of the 2008 8-hour ozone
NAAQS in other states. Chapters 62–296
and 62–297 establish emission
standards and compliance (testing and
monitoring) requirements respectively
for stationary sources of air pollution
emissions.
Based on the information presented
herein, EPA proposes to approve
Florida’s SIP submission on grounds
that it addresses the State’s
110(a)(2)(D)(i)(I) good neighbor
obligation for the 2008 8-hour ozone
NAAQS because the EPA has found that
the State will not significantly
contribute to nonattainment or interfere
with maintenance of the 2008 ozone
NAAQS in any other state.
III. Proposed Action
EPA is proposing to approve Florida’s
October 3, 2017 SIP submission
demonstrating that Florida’s SIP is
sufficient to address the CAA
requirements of prongs 1 and 2 under
section 110(a)(2)(D)(i)(I) for the 2008 8hour ozone NAAQS. In the CSAPR
Update, EPA has already taken a final
action to determine that emissions from
Florida will not significantly contribute
to nonattainment or interfere with
15 See Florida’s October 3, 2017, SIP submission,
Appendix 1 for additional information on ozone
precursor emission trends and monitored ozone
concentrations in the State.
E:\FR\FM\15FEP1.SGM
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Federal Register / Vol. 84, No. 32 / Friday, February 15, 2019 / Proposed Rules
khammond on DSKBBV9HB2PROD with PROPOSALS
maintenance of the 2008
8-hour ozone NAAQS in downwind
states. EPA requests comment on this
proposed approval of Florida’s SIP.16
IV. Statutory and Executive Order
Reviews
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
Act and applicable federal regulations.
See 42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this proposed
action merely proposes to approve state
law as meeting federal requirements and
does not impose additional
requirements beyond those imposed by
state law. For that reason, this proposed
action:
• Is not a significant regulatory action
subject to review by the Office of
Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• is not an Executive Order 13771 (82
FR 9339, February 2, 2017) regulatory
action because SIP approvals are
exempted under Executive Order 12866;
• does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the Clean Air Act;
and
• does not provide EPA with the
discretionary authority to address, as
16 EPA is not reopening for comment final
determinations made in the CSAPR Update or the
modeling conducted to support that rulemaking.
VerDate Sep<11>2014
17:13 Feb 14, 2019
Jkt 247001
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 as specified by Executive
Order 13175 (65 FR 67249, November 9,
2000), nor will it impose substantial
direct costs on tribal governments or
preempt tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Nitrogen oxides, Ozone, Reporting and
recordkeeping requirements, Volatile
organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: February 5, 2019.
Mary S. Walker,
Acting Regional Administrator, Region 4.
[FR Doc. 2019–02542 Filed 2–14–19; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R04–OAR–2018–0799; FRL–9989–58–
Region 4]
Air Plan Approval; Kentucky; Regional
Haze Plan and Prong 4 (Visibility) for
the 1997 Ozone, 2010 NO2, 2010 SO2,
and 2012 PM2.5 NAAQS
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
The Environmental Protection
Agency (EPA) is proposing to take the
following four actions regarding the
Kentucky State Implementation Plan
(SIP): Approve Kentucky’s November
16, 2018, SIP submittal seeking to
change reliance from the Clean Air
Interstate Rule (CAIR) to the Cross-State
Air Pollution Rule (CSAPR) for certain
regional haze requirements; convert
EPA’s limited approval/limited
disapproval of Kentucky’s regional haze
plan to a full approval; remove EPA’s
Federal Implementation Plan (FIP) for
Kentucky which replaced reliance on
CAIR with reliance on CSAPR to
address the deficiencies identified in
the limited disapproval of Kentucky’s
regional haze plan; and approve the
visibility prong of Kentucky’s
SUMMARY:
PO 00000
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Fmt 4702
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4407
infrastructure SIP submittals for the
1997 Ozone, 2010 Nitrogen Dioxide
(NO2), 2010 Sulfur Dioxide (SO2), and
2012 Fine Particulate Matter (PM2.5)
National Ambient Air Quality Standards
(NAAQS).
DATES: Comments must be received on
or before March 18, 2019.
ADDRESSES: Submit your comments,
identified by Docket ID No EPA–R04–
OAR–2018–0799 at https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Once submitted, comments cannot be
edited or removed from Regulations.gov.
EPA may publish any comment received
to its public docket. Do not submit
electronically any information you
consider to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Multimedia submissions (audio, video,
etc.) must be accompanied by a written
comment. The written comment is
considered the official comment and
should include discussion of all points
you wish to make. EPA will generally
not consider comments or comment
contents located outside of the primary
submission (i.e., on the web, cloud, or
other file sharing system). For
additional submission methods, the full
EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www2.epa.gov/dockets/
commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT:
Michele Notarianni, Air Regulatory
Management Section, Air, Pesticides
and Toxics Management Division, U.S.
Environmental Protection Agency,
Region 4, 61 Forsyth Street SW, Atlanta,
Georgia 30303–8960. Ms. Notarianni can
be reached by telephone at (404) 562–
9031 or via electronic mail at
notarianni.michele@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
A. Regional Haze Plans and Their
Relationship With CAIR and CSAPR
Section 169A(b)(2)(A) of the Clean Air
Act (CAA or Act) requires states to
submit regional haze plans that contain
such measures as may be necessary to
make reasonable progress towards the
natural visibility goal, including a
requirement that certain categories of
existing major stationary sources built
between 1962 and 1977 procure, install,
and operate Best Available Retrofit
Technology (BART) as determined by
the state. Under the Regional Haze Rule
(RHR), states are directed to conduct
BART determinations for such ‘‘BART-
E:\FR\FM\15FEP1.SGM
15FEP1
Agencies
[Federal Register Volume 84, Number 32 (Friday, February 15, 2019)]
[Proposed Rules]
[Pages 4403-4407]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-02542]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R04-OAR-2018-0542; FRL-9989-59-Region 4]
Air Plan Approval; Florida; 2008 8-Hour Ozone Interstate
Transport
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is proposing to
approve Florida's October 3, 2017, State Implementation Plan (SIP)
submission pertaining to the ``good neighbor'' provision of the Clean
Air Act (CAA or Act) for the 2008 8-hour ozone National Ambient Air
Quality Standards (NAAQS). The good neighbor provision requires each
state's implementation plan to address the interstate transport of air
pollution in amounts that contribute significantly to nonattainment, or
interfere with maintenance of a NAAQS in any other state. In this
action, EPA is proposing to determine that Florida's SIP contains
adequate provisions to prohibit emissions within the state from
contributing significantly to nonattainment or interfering with
maintenance of the 2008 8-hour ozone NAAQS in any other state.
DATES: Comments must be received on or before March 18, 2019.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R04-
OAR-2018-0542 at https://www.regulations.gov. Follow the online
instructions for submitting comments. Once submitted, comments cannot
be edited or removed from regulations.gov. EPA may publish any comment
received to its public docket. Do not submit electronically any
information you consider to be Confidential Business Information (CBI)
or other information whose disclosure is restricted by statute.
Multimedia submissions (audio, video, etc.) must be accompanied by a
written comment. The written comment is considered the official comment
and should include discussion of all points you wish to make. EPA will
generally not consider comments or comment contents located outside of
the primary submission (i.e., on the web, cloud, or other file sharing
system). For additional submission methods, the full EPA public comment
policy, information about CBI or multimedia submissions, and general
guidance on making effective comments, please visit https://www2.epa.gov/dockets/commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT: Nacosta C. Ward, Air Regulatory
Management Section, Air Planning and Implementation Branch, Air,
Pesticides and Toxics Management Division, U.S. Environmental
Protection Agency, Region 4, 61 Forsyth Street SW, Atlanta, Georgia
30303-8960. Ms. Ward can also be reached via telephone at (404) 562-
9140 and via electronic mail at ward.nacosta@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
On March 12, 2008, EPA promulgated an ozone NAAQS that revised the
levels of the primary and secondary 8-hour ozone standards from 0.08
parts per
[[Page 4404]]
million (ppm) to 0.075 ppm.\1\ See 73 FR 16436 (March 27, 2008).
Pursuant to CAA section 110(a)(1), within three years after
promulgation of a new or revised NAAQS (or shorter, if EPA prescribes),
states must submit SIPs that meet the applicable requirements of
section 110(a)(2). EPA has historically referred to these SIP
submissions made for the purpose of satisfying the requirements of
sections 110(a)(1) and 110(a)(2) as ``infrastructure SIP'' submissions.
One of the structural requirements of section 110(a)(2) is section
110(a)(2)(D)(i), which generally requires SIPs to contain adequate
provisions to prohibit in-state emissions activities from having
certain adverse air quality effects on neighboring states due to
interstate transport of air pollution. There are four sub-elements, or
``prongs,'' within section 110(a)(2)(D)(i) of the CAA. CAA section
110(a)(2)(D)(i)(I), also known as the ``good neighbor'' provision,
requires SIPs to include provisions prohibiting any source or other
type of emissions activity in one state from emitting any air pollutant
in amounts that will contribute significantly to nonattainment, or
interfere with maintenance, of the NAAQS in another state. The two
provisions of this section are referred to as prong 1 (significant
contribution to nonattainment) and prong 2 (interference with
maintenance). Section 110(a)(2)(D)(i)(II) requires SIPs to contain
adequate provisions to prohibit emissions that will interfere with
measures required to be included in the applicable implementation plan
for any other state under part C to prevent significant deterioration
of air quality (prong 3) or to protect visibility (prong 4). This
proposed action addresses only prongs 1 and 2 of section
110(a)(2)(D)(i). All other infrastructure SIP elements for Florida for
the 2008 8-hour ozone NAAQS were addressed in separate rulemakings.\2\
---------------------------------------------------------------------------
\1\ 0.075 ppm equates to 75 parts per billion (ppb).
\2\ See 78 FR 65559 (November 1, 2013); 79 FR 50554 (August 25,
2014).
---------------------------------------------------------------------------
A. State Submittal
On October 3, 2017, the Florida Department of Environmental
Protection (FDEP) provided a SIP submittal \3\ to EPA to address the
interstate transport requirements of sections 110(a)(2)(D)(i)(I) for
the Florida SIP. Florida made this submission to certify that its SIP
contains adequate provisions to prohibit emissions activities within
the State which will contribute significantly to nonattainment or
interfere with maintenance of the 2008 8-hour ozone NAAQS in any other
state, and therefore, adequately addresses the requirements of CAA
section 110(a)(2)(D)(i)(I) for the 2008 8-hour ozone NAAQS.\4\
Florida's certification is based on emissions generating activities,
air quality monitoring and modeling data, and SIP-approved and state
provisions regulating emissions of ozone precursors (volatile organic
compounds (VOCs) and nitrogen oxides (NOX)) within the
State.
---------------------------------------------------------------------------
\3\ This submittal supplements an October 31, 2011 submittal
addressing other infrastructure SIP elements for Florida for the
2008 Ozone NAAQS. See 78 FR 65559, 79 FR 50554. Although the
transmittal letter is dated October 3, 2017, EPA did not receive
Florida's submittal until October 12, 2017.
\4\ On July 13, 2015, EPA published a final rule that finalized
findings of failure to submit with regard to the requirements of CAA
section 110(a)(2)(D)(i)(I) for 24 states, including Florida, with
respect to the 2008 ozone NAAQS. See 80 FR 39961. The findings of
failure to submit established a two-year deadline for EPA to
promulgate a FIP to address the interstate transport SIP
requirements pertaining to significant contribution to nonattainment
and interference with maintenance unless, prior to EPA promulgating
a FIP, the state submits, and EPA approves, a SIP that meets these
requirements. Additional background on the findings of failure to
submit--including Florida's finding--can be found in the preamble to
the final rule findings.
---------------------------------------------------------------------------
B. EPA's Analysis Related to 110(a)(2)(D)(i)(I) for the 2008 8-Hour
Ozone NAAQS
EPA developed technical information and related analyses to assist
states with meeting section 110(a)(2)(D)(i)(I) requirements for the
2008 8-hour ozone NAAQS through SIPs and, as appropriate, to provide
backstop federal implementation plans (FIPs) in the event that states
failed to submit approvable SIPs.\5\ On October 26, 2016 (81 FR 74504),
EPA took steps to effectuate this backstop role with respect to eastern
states \6\ by finalizing an update to the Cross-State Air Pollution
Rule (CSAPR) ozone season program that addresses good neighbor
obligations for the 2008 8-hour ozone NAAQS (``CSAPR Update''). The
CSAPR Update establishes statewide NOX budgets for certain
affected electricity generating units in 22 eastern states for the May-
September ozone season to reduce the interstate transport of ozone
pollution in the eastern United States, and thereby help downwind
states and communities meet and maintain the 2008 8-hour ozone NAAQS.
See 81 FR 74506. The rule also determined that emissions from 14 states
(including Florida) will not significantly contribute to nonattainment
or interfere with maintenance of the 2008 ozone NAAQS in downwind
states. Accordingly, EPA determined that it need not require further
emission reductions from sources in those states to address the good
neighbor provision as to the 2008 ozone NAAQS. Id.
---------------------------------------------------------------------------
\5\ The EPA issued a Notice of Data Availability on August 4,
2015 requesting comment on the modeling platform and air quality
modeling results that were used for the proposed CSAPR Update. See
80 FR 46271.
\6\ For purposes of the CSAPR Update, ``eastern'' states refer
to all contiguous states fully east of the Rocky Mountains (thus not
including the mountain states of Montana, Wyoming, Colorado, or New
Mexico).
---------------------------------------------------------------------------
The CSAPR Update used the same framework that EPA used when
developing the original 2011 CSAPR, EPA's interstate transport rule
addressing the 1997 8-hour ozone NAAQS as well as the 1997 and 2006
fine particulate matter (PM2.5) NAAQS. The CSAPR framework
establishes the following four-step process to address the requirements
of the good neighbor provision: (1) Identify downwind areas, referred
to as receptors, that are expected to have problems attaining or
maintaining the NAAQS; (2) determine which upwind states impact these
identified problems in amounts sufficient to ``link'' them to the
downwind air quality problems; (3) for states linked to downwind air
quality problems, identify upwind emissions, if any, that will
significantly contribute to nonattainment or interfere with maintenance
of a NAAQS; and (4) reduce the identified upwind emissions for states
that are found to have emissions that will significantly contribute to
nonattainment or interfere with maintenance of the NAAQS downwind by
adopting permanent and enforceable measures in a FIP or SIP. In the
CSAPR Update, EPA used this four-step framework to determine whether
states in the east will significantly contribute to nonattainment or
interference with maintenance of downwind air quality. As explained
below, the CSAPR Update's four-step analysis supports the conclusions
provided in FDEP's October 3, 2017, interstate transport SIP for the
2008 8-hour ozone NAAQS that the State will not significantly
contribute to nonattainment or interfere with maintenance of the
standard in other states.
In the technical analysis supporting the CSAPR Update, EPA used
detailed air quality analyses to determine where projected
nonattainment or maintenance receptors would be, at step 1 of the four-
step framework, and whether emissions from an eastern state contribute
to downwind air quality problems at those projected nonattainment or
maintenance receptors, at step 2 of the framework. Specifically, EPA
determined whether each state's contributing emissions were
[[Page 4405]]
at or above a specific threshold (i.e., one percent of the ozone
NAAQS). EPA determined that one percent was an appropriate threshold to
use in this analysis because there were important, even if relatively
small, contributions to identified nonattainment and maintenance
receptors from multiple upwind states at that threshold.\7\ See 81 FR
74504 (October 26, 2016). For the CSAPR Update, EPA applied an air
quality screening threshold of 0.75 ppb (one percent of the 2008 8-hour
ozone NAAQS of 75 ppb) to identify linkages between upwind states and
the downwind nonattainment and maintenance receptors. States with
impacts below the one-percent threshold were considered not to
contribute to identified downwind nonattainment and maintenance
receptors and therefore would not contribute significantly to
nonattainment or interfere with maintenance of the standard in those
downwind areas. If a state's impact was equal to or exceeded the one-
percent threshold, that state was considered ``linked'' to the downwind
nonattainment or maintenance receptor(s) and the state's emissions were
further evaluated, taking into account both air quality and cost
considerations, to determine whether any emissions reductions might be
necessary to address the state's obligation pursuant to CAA section
110(a)(2)(D)(i)(I).
---------------------------------------------------------------------------
\7\ EPA's analysis showed that the one-percent threshold
generally captured a high percentage of the total pollution
transport affecting downwind states. EPA's analysis further showed
that the application of a lower threshold would result in relatively
modest increases in the overall percentage of ozone transport
pollution captured, while the use of higher thresholds would result
in a relatively large reduction in the overall percentage of ozone
pollution transport captured relative to the levels captured at one
percent at the majority of the receptors. See 81 FR 74504 (October
26, 2016) and ``Air Quality Modeling Final Rule Technical Support
Document for the Final CSAPR Update'' (CSAPR Update Modeling TSD),
available at https://www.epa.gov/sites/production/files/2017-05/documents/aq_modeling_tsd_final_csapr_update.pdf. This approach is
consistent with the use of a one-percent threshold to identify those
states ``linked'' to air quality problems with respect to the 1997
8-hour ozone NAAQS in the original CSAPR rulemaking, wherein EPA
noted that there are adverse health impacts associated with ambient
ozone even at low levels. See 76 FR 48208 (August 8, 2011). See
technical support document for the August 8, 2011 final rule
``Federal Implementation Plans: Interstate Transport of Fine
Particulate Matter and Ozone and Correction of SIP'' approvals''
located at https://www.regulations.gov/document?D=EPA-HQ-OAR-2009-0491-4140.
---------------------------------------------------------------------------
As discussed in the final rule for the CSAPR Update, the air
quality modeling contained in EPA's technical analysis: (1) Identified
locations in the U.S. where EPA anticipated nonattainment or
maintenance issues in 2017 for the 2008 8-hour ozone NAAQS (these were
identified as nonattainment or maintenance receptors, respectively),
and (2) quantified the projected contributions from emissions from
upwind states to downwind ozone concentrations at the receptors in
2017. See 81 FR 74504 (October 26, 2016). This modeling used the
Comprehensive Air Quality Model with Extensions (CAMx
version 6.11) to model the 2011 base year and the 2017 future base case
emissions scenarios to identify projected nonattainment and maintenance
sites with respect to the 2008 8-hour ozone NAAQS in 2017. EPA used
nationwide state-level ozone source apportionment modeling (the
CAMx Ozone Source Apportionment Technology/Anthropogenic
Precursor Culpability Analysis technique) to quantify the contribution
of 2017 base case NOX and VOC emissions from all sources in
each state to the 2017 projected receptors. The air quality model runs
were performed for a modeling domain that covers the 48 contiguous
United States, the District of Columbia, and adjacent portions of
Canada and Mexico. The updated modeling data released to support the
final CSAPR Update for Florida are the most up-to-date information EPA
has developed to inform the Agency's analysis of upwind state linkages
to downwind air quality problems for the 2008 8-hour ozone NAAQS. See
``Air Quality Modeling Final Rule Technical Support Document for the
Final CSAPR Update'' (CSAPR Update Modeling TSD).\8\
---------------------------------------------------------------------------
\8\ See ``Air Quality Modeling Final Rule Technical Support
Document for the Final CSAPR Update'' (CSAPR Update Modeling TSD),
available at https://www.epa.gov/sites/production/files/2017-05/documents/aq_modeling_tsd_final_csapr_update.pdf.
---------------------------------------------------------------------------
EPA's air quality modeling for the final CSAPR Update indicated
that Florida's largest impact on any projected downwind nonattainment
receptor in 2017 was 0.71 ppb, which is below the one-percent
threshold. Accordingly, Florida is not ``linked'' to any nonattainment
receptors in EPA's modeling. Although the modeling for the proposed
CSAPR Update did not link Florida's emissions to any maintenance
receptors, the updated modeling conducted for the final CSAPR Update
indicated that Florida's largest contribution to any projected downwind
maintenance-only site in 2017 would be 0.75 ppb.\9\ EPA's modeling
indicated an average contribution at the 0.75 ppb threshold to the 2017
design values at two receptors in Houston, Texas (i.e., Harris County
sites 482010024 and 482011034).
---------------------------------------------------------------------------
\9\ See CSAPR Update Modeling TSD at Table 4-2, section 4.4 and
Appendix D located at available at https://www.epa.gov/sites/production/files/2017-05/documents/aq_modeling_tsd_final_csapr_update.pdf.
---------------------------------------------------------------------------
EPA received a comment on the CSAPR Update proposal \10\ stating
that the version of CAMx used for the proposal modeling
(CAMx v6.11) did not include the most recent halogen
chemistry that would affect ozone concentrations in saltwater marine
atmospheres and transport of ozone from Florida to receptors in Texas.
The commenter stated that EPA should include this chemistry in modeling
for the final rule. See 81 FR 74504 (October 26, 2016). A report by the
CAMx model developer on the impact of modeling with the
latest CAMx halogen chemistry indicates that the updated
chemistry results in lower modeled ozone in air transported over
saltwater marine environments for multiple days.\11\ Specifically, the
report notes that on days with multi-day transport across the Gulf of
Mexico, modeling with the updated chemistry could lower 8-hour daily
maximum ozone concentrations by up to 2 to 4 ppb in locations in
eastern Texas, including Houston. Air parcel trajectories for
individual days used in EPA's calculation of the contribution from
Florida to the Houston receptors confirm that on days with high modeled
transport from Florida to the receptors in Houston, air travels for
multiple days over the Gulf of Mexico from Florida before reaching the
receptors in Houston.\12\ In the final rule modeling, EPA was not able
to explicitly account for the updated chemistry because this chemistry
had not yet been included by the model developer in the source
apportionment tool in CAMx at the time the modeling was
performed for this rule. However, because Florida's maximum impact on
receptors in Houston, Texas, is exactly
[[Page 4406]]
at the 0.75 ppb threshold, the Agency concluded that if it had
performed the final rule modeling with the updated halogen chemistry,
Florida's impact would likely be below this threshold. Therefore, EPA
determined in the CSAPR Update that when this updated halogen chemistry
is considered, there are no identified linkages between Florida and
2017 downwind projected nonattainment and maintenance receptors. As a
result of the modeling, EPA did not finalize a FIP that required
NOX emission reductions from Florida in the CSAPR Update
because EPA's analysis performed to support the final rule does not
indicate that the State is linked to any identified downwind
nonattainment or maintenance receptors with respect to the 2008 8-hour
ozone NAAQS. Rather, in the CSAPR Update, EPA took final action to
determine that emissions from Florida will not significantly contribute
to nonattainment or interfere with maintenance of the 2008 8-hour ozone
NAAQS in any other states.
---------------------------------------------------------------------------
\10\ See 80 FR 75706 (December 3, 2015).
\11\ See Yarwood, G., T. Sakulyanontvittaya, O. Nopmongcol, and
B. Koo, 2014. Ozone Depletion by Bromine and Iodine over the Gulf of
Mexico Final Report. Prepared for the Texas Commission on
Environmental Quality. November 2014. Ramboll Environ International
Corporation, Novato, CA and Yarwood, G., J. Jung, O. Nopmongcol, and
C. Emery, 2012. Improving CAMx Performance in Simulating
Ozone Transport from the Gulf of Mexico. Prepared for the Texas
Commission on Environmental Quality. September 2012. Ramboll Environ
International Corporation, Novato, CA. These studies are available
in the docket for the CSAPR Update Rule as EPA-HQ-OAR-2015-0500-0458
and EPA-HQ-OAR-2015-0500-0457, respectively.
\12\ More details and analysis of the impact of the
CAMx halogen chemistry updates on the contributions from
Florida and other Gulf Coast states can be found in section 4.4 and
Appendix D to the CSAPR Update Modeling TSD available at https://www.epa.gov/sites/production/files/2017-05/documents/aq_modeling_tsd_final_csapr_update.pdf.
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Additionally, the CSAPR Update addressed the decision from the
United States Court of Appeals for the District of Columbia Circuit in
EME Homer City Generation, L.P. v. EPA, 795 F.3d 118 (D.C. Cir. 2015),
remanding for reconsideration certain states' ozone season
NOX emission budgets from the original CSAPR (including
Florida's) with respect to the 1997 8-hour ozone NAAQS.\13\ EPA removed
Florida from the CSAPR ozone season trading program beginning in
2017.\14\
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\13\ Among other things, the decision remanded CSAPR without
vacatur for reconsideration of the EPA's emission budgets for
certain states. The court declared invalid the CSAPR Phase 2
NOX ozone season emission budgets of 11 states, including
Florida, holding that those budgets over-control with respect to the
downwind air quality problems to which those states were linked for
the 1997 ozone NAAQS. Because the 2008 ozone NAAQS is more stringent
than the 1997 ozone NAAQS, the CSAPR Update modeling necessarily
indicates that Florida is also not linked to any remaining air
quality concerns with respect to the 1997 ozone standard for which
the states were regulated in the original CSAPR. For Florida, EPA
therefore relieved sources in the State from the obligation to
comply with the NOX ozone season trading program in
response to the remand. The court also remanded without vacatur the
CSAPR Phase 2 SO2 annual emission budgets for four states
(Alabama, Georgia, South Carolina, and Texas) for reconsideration.
\14\ See 81 FR 74523-74524, October 26, 2016.
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II. What is EPA's analysis of the Florida submittal?
As mentioned in section I of this document, Florida's October 3,
2017 submittal certifies that emission activities from the State will
not contribute significantly to nonattainment or interfere with
maintenance of the 2008 8-hour ozone NAAQS in any other state for the
following reasons: (1) Modeling conducted by EPA in support of the
CSAPR Update indicates that Florida's impact on any downwind receptor
is less than one percent of the standard; (2) NOX and VOC
precursor emissions and monitored ozone concentrations in Florida have
decreased since 2000; and (3) Florida has SIP-approved stationary
source emissions standards and monitoring and permitting regulations in
place addressing certain emissions generating activities that
contribute to ozone precursor emissions. Based on an assessment of this
information, EPA proposes to approve Florida's SIP submission because
it has adequate provisions to ensure that emissions from sources within
the State will not significantly contribute to nonattainment or
interfere with maintenance of the 2008 8-hour ozone NAAQS in any other
state.
Florida's submittal assessed EPA's CSAPR Update modeling that
showed Florida's contribution to downwind receptors for the 2008 8-hour
ozone NAAQS is less than one percent of the standard (i.e., 0.75 ppb),
except as follows. As discussed in Florida's October 3, 2017 SIP
submission, the CSAPR Update 2017 modeling generated an average
contribution from Florida at the 0.75 ppb threshold to two receptors in
Houston, Texas (i.e., Harris County sites 482010024 and 482011034).
However, as discussed in section I.B of this document and the CSAPR
Update, a newer version of the CAMx chemical mechanism
contains updated chemical reactions (halogen chemistry) which may have
an impact on the estimated ozone contributions from Florida emissions
to Houston receptors. In the final rule modeling, EPA was not able to
explicitly account for the updated chemistry because this chemistry had
not yet been included by the model developer in the source
apportionment tool in CAMx at the time the modeling was
performed for this final rule. However, because Florida's maximum
contribution to receptors in Houston, Texas is exactly at the 0.75 ppb
threshold, the Agency believes that if it had performed the final rule
modeling with the updated halogen chemistry, Florida's contribution
would likely be below the 0.75 ppb threshold. Therefore, EPA concluded
that Florida's emissions will not contribute to downwind nonattainment
and maintenance receptors when considering updated halogen chemistry
and therefore, did not finalize a FIP that required NOX
emission reductions from Florida in the CSAPR Update. Accordingly, in
the CSAPR Update, EPA already made a final determination that Florida
emissions will not significantly contribute to nonattainment or
interfere with the 2008 ozone NAAQS in other states and that sources in
the State are not required to further reduce emissions pursuant to the
good neighbor provision with respect to this standard.
Florida's submittal also notes that total NOX and non-
biogenic VOC emissions in Florida have decreased by 52 percent and 44
percent, respectively, since 2000. Florida indicates that monitored
ozone concentrations in the State are also trending downward, which
correlates to the decline in ozone precursor emissions.\15\
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\15\ See Florida's October 3, 2017, SIP submission, Appendix 1
for additional information on ozone precursor emission trends and
monitored ozone concentrations in the State.
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Florida also identified SIP-approved regulations in the Florida
Administrative Code, including Chapters 62-204, 62-210, and 62-212,
that provide for the implementation of a permitting program required
under title I, parts C and D of the CAA for sources of NOX
and VOC ozone precursors that contribute to ambient ozone
concentrations. The permitting requirements help ensure that no new or
modified sources in the State subject to these permitting regulations
will contribute significantly to nonattainment or interfere with
maintenance of the 2008 8-hour ozone NAAQS in other states. Chapters
62-296 and 62-297 establish emission standards and compliance (testing
and monitoring) requirements respectively for stationary sources of air
pollution emissions.
Based on the information presented herein, EPA proposes to approve
Florida's SIP submission on grounds that it addresses the State's
110(a)(2)(D)(i)(I) good neighbor obligation for the 2008 8-hour ozone
NAAQS because the EPA has found that the State will not significantly
contribute to nonattainment or interfere with maintenance of the 2008
ozone NAAQS in any other state.
III. Proposed Action
EPA is proposing to approve Florida's October 3, 2017 SIP
submission demonstrating that Florida's SIP is sufficient to address
the CAA requirements of prongs 1 and 2 under section 110(a)(2)(D)(i)(I)
for the 2008 8-hour ozone NAAQS. In the CSAPR Update, EPA has already
taken a final action to determine that emissions from Florida will not
significantly contribute to nonattainment or interfere with
[[Page 4407]]
maintenance of the 2008 8-hour ozone NAAQS in downwind states. EPA
requests comment on this proposed approval of Florida's SIP.\16\
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\16\ EPA is not reopening for comment final determinations made
in the CSAPR Update or the modeling conducted to support that
rulemaking.
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IV. Statutory and Executive Order Reviews
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the Act and applicable
federal regulations. See 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
proposed action merely proposes to approve state law as meeting federal
requirements and does not impose additional requirements beyond those
imposed by state law. For that reason, this proposed action:
Is not a significant regulatory action subject to review
by the Office of Management and Budget under Executive Orders 12866 (58
FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21, 2011);
is not an Executive Order 13771 (82 FR 9339, February 2,
2017) regulatory action because SIP approvals are exempted under
Executive Order 12866;
does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
does not have Federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
is not subject to requirements of Section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the Clean Air Act; and
does not provide 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 as specified by Executive Order 13175 (65
FR 67249, November 9, 2000), nor will it impose substantial direct
costs on tribal governments or preempt tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Intergovernmental relations, Nitrogen oxides, Ozone,
Reporting and recordkeeping requirements, Volatile organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: February 5, 2019.
Mary S. Walker,
Acting Regional Administrator, Region 4.
[FR Doc. 2019-02542 Filed 2-14-19; 8:45 am]
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