Air Plan Approval; Indiana; Reasonable Further Progress Plan and Other Plan Elements for the Chicago Nonattainment Area for the 2008 Ozone Standard, 43825-43836 [2018-18640]
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Federal Register / Vol. 83, No. 167 / Tuesday, August 28, 2018 / Proposed Rules
(4) State each reason why the troubled
institution cannot meet the standard set
forth in § 1231.3(e)(2).
(f) Waiver of form or content
requirements. FHFA may waive or
modify any requirement related to the
form or content of a request or notice,
in circumstances deemed appropriate by
FHFA.
(g) Additional information. FHFA
may request additional information at
any time during the processing of the
request or after receiving a notice.
Dated: August 20, 2018.
Melvin L. Watt,
Director, Federal Housing Finance Agency.
[FR Doc. 2018–18511 Filed 8–27–18; 8:45 am]
BILLING CODE 8070–01–P
DEPARTMENT OF LABOR
Wage and Hour Division
29 CFR Part 541
White Collar Exemption Regulations;
Public Listening Sessions
Wage and Hour Division,
Department of Labor.
ACTION: Notification of public listening
sessions.
AGENCY:
The Department of Labor will
conduct public listening sessions to
gather views on white collar exemption
regulations. The Fair Labor Standards
Act (FLSA) generally requires covered
employers to pay their employees at
least the federal minimum wage
(currently $7.25 an hour) for all hours
worked, and overtime premium pay of
not less than one and one-half times the
employee’s regular rate of pay for any
hours worked over 40 in a workweek.
The FLSA exempts from both minimum
wage and overtime protection ‘‘any
employee employed in a bona fide
executive, administrative, or
professional capacity’’ and delegates to
the Secretary of Labor the power to
define and delimit these terms through
regulation.
DATES: The dates, locations, and times
for the public listening sessions are
listed below:
September 7, 2018, Atlanta, Georgia, 10
a.m.–12 p.m.
September 11, 2018, Seattle,
Washington, 10 a.m.–12 p.m.
September 13, 2018, Kansas City,
Missouri, 10 a.m.–12 p.m.
September 14, 2018, Denver, Colorado,
10 a.m.–12 p.m.
September 24, 2018, Providence, Rhode
Island, 10 a.m.–12 p.m.
Members of the public may attend
these listening sessions in person up to
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the seating capacity of the room. The
Department will not attempt to achieve
a consensus view in these listening
sessions, but rather is interested in
hearing the views and ideas of
participants.
To obtain specific location
details and register to attend, please
visit this link: https://
www.eventbrite.com/e/overtime-ruleoutreach-sessions-tickets-49216139799.
FOR FURTHER INFORMATION CONTACT:
Stephen Davis, Listening Session
Coordinator, Division of Regulations,
Legislation, and Interpretation, Wage
and Hour Division, U.S. Department of
Labor, Room S–3502, 200 Constitution
Avenue NW, Washington, DC 20210;
telephone: (202) 693–0406 (this is not a
toll-free number). Copies of this notice
may be obtained in alternative formats
(Large Print, Braille, Audio Tape, or
Disc), upon request, by calling (202)
693–0023 (not a toll-free number). TTY/
TTD callers may dial toll-free (877) 889–
5627 to obtain information or request
materials in alternative formats.
SUPPLEMENTARY INFORMATION: On July
26, 2017, the Department of Labor
published a Request for Information
(RFI), Defining and Delimiting the
Exemptions for Executive,
Administrative, Professional, Outside
Sales and Computer Employees. See 82
FR 34616. The RFI was one opportunity
for the public to provide information to
aid the Department in formulating a
proposal to revise the white collar
exemption regulations. Public listening
sessions will provide further
opportunity for the public to provide
input on issues related to the salary
level test, such as:
1. What is the appropriate salary level
(or range of salary levels) above which
the overtime exemptions for bona fide
executive, administrative, or
professional employees may apply?
Why?
2. What benefits and costs to
employees and employers might
accompany an increased salary level?
How would an increased salary level
affect real wages (e.g., increasing
overtime pay for employees whose
current salaries are below a new level
but above the current threshold)? Could
an increased salary level reduce
litigation costs by reducing the number
of employees whose exemption status is
unclear? Could this additional certainty
produce other benefits for employees
and employers?
3. What is the best methodology to
determine an updated salary level?
Should the update derive from wage
growth, cost-of-living increases, actual
ADDRESSES:
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wages paid to employees, or some other
measure?
4. Should the Department more
regularly update the standard salary
level and the total-annual-compensation
level for highly compensated
employees? If so, how should these
updates be made? How frequently
should updates occur? What benefits, if
any, could result from more frequent
updates?
Dated: August 23, 2018.
Melissa Smith,
Director, Division of Regulations, Legislation
and Interpretation.
[FR Doc. 2018–18649 Filed 8–27–18; 8:45 am]
BILLING CODE 4510–27–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R05–OAR–2017–0147; FRL–9982–
90—Region 5]
Air Plan Approval; Indiana;
Reasonable Further Progress Plan and
Other Plan Elements for the Chicago
Nonattainment Area for the 2008
Ozone Standard
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
The Environmental Protection
Agency (EPA) is proposing to approve a
revision to the Indiana State
Implementation Plan (SIP) to meet the
base year emissions inventory,
reasonable further progress (RFP), RFP
contingency measure, nonattainment
new source review (nonattainment
NSR), volatile organic compound (VOC)
reasonably available control technology
(RACT), and motor vehicle inspection
and maintenance (I/M) requirements of
the Clean Air Act (CAA) for the Indiana
portion of the Chicago-Naperville,
Illinois-Indiana-Wisconsin area
(Chicago area) for the 2008 ozone
national ambient air quality standard
(NAAQS or standard). EPA is also
proposing to approve the 2017
transportation conformity motor vehicle
emissions budgets (MVEBs) for the
Indiana portion of the Chicago area for
the 2008 ozone NAAQS. EPA is
proposing to approve the state’s
submission as a SIP revision pursuant to
section 110 and part D of the CAA and
EPA’s regulations because it satisfies the
emission inventory, RFP, RFP
contingency measure, nonattainment
NSR, VOC RACT, I/M, and
transportation conformity requirements
for areas classified as moderate
SUMMARY:
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nonattainment for the 2008 ozone
NAAQS. Final approval of Indiana’s SIP
as meeting the nonattainment NSR
requirements of the CAA for the 2008
ozone NAAQS will permanently stop
the sanctions and Federal
Implementation Plan (FIP) clocks
triggered by EPA’s February 3, 2017
finding that Indiana failed to submit a
marginal ozone nonattainment NSR
plan.
DATES: Comments must be received on
or before September 27, 2018.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2017–0147, at https://
www.regulations.gov, or via email to
Aburano.Douglas@epa.gov. For
comments submitted at Regulations.gov,
follow the online instructions for
submitting comments. Once submitted,
comments cannot be edited or removed
from Regulations.gov. For either manner
of submission, 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, please contact the person
identified in the FOR FURTHER
INFORMATION CONTACT section. For 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:
Kathleen D’Agostino, Environmental
Engineer, Attainment Planning and
Maintenance Section, Air Programs
Branch (AR–18J), U.S. Environmental
Protection Agency, Region 5, 77 West
Jackson Boulevard, Chicago, Illinois
60604, (312) 886–1767,
Dagostino.Kathleen@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
EPA. This supplementary information
section is arranged as follows:
I. What is the background for this action?
II. What is EPA’s evaluation of Indiana’s
submittal?
III. What action is EPA proposing?
IV. Statutory and Executive Order Reviews
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I. What is the background for this
action?
A. Background on the 2008 Ozone
Standard
On March 12, 2008, EPA promulgated
a revised 8-hour ozone NAAQS of 0.075
parts per million (ppm).1 Promulgation
of a revised NAAQS triggers a
requirement for EPA to designate all
areas of the country as nonattainment,
attainment, or unclassifiable for the
NAAQS. For the ozone NAAQS, this
also involves classifying any
nonattainment areas at the time of
designation.2 Ozone nonattainment
areas are classified based on the severity
of their ozone levels (as determined
based on the area’s ‘‘design value,’’
which represents air quality in the area
for the most recent 3 years). The
classifications for ozone nonattainment
areas are marginal, moderate, serious,
severe, and extreme.3
Areas that EPA designates
nonattainment for the ozone NAAQS are
subject to the general nonattainment
area planning requirements of CAA
section 172 and also to the ozonespecific planning requirements of CAA
section 182. Ozone nonattainment areas
in the lower classification levels have
fewer and/or less stringent mandatory
air quality planning and control
requirements than those in higher
classifications. For marginal areas, a
state is required to submit a baseline
emissions inventory, adopt provisions
into the SIP requiring emissions
statements from stationary sources, and
implement a nonattainment NSR
program for the relevant ozone
NAAQS.4 For moderate areas, a state
needs to comply with the marginal area
requirements, plus additional moderate
area requirements, including the
requirement to submit a modeled
demonstration that the area will attain
the NAAQS as expeditiously as
practicable but no later than 6 years
after designation, the requirement to
submit an RFP plan, the requirement to
adopt and implement certain emissions
controls, such as RACT and I/M, and the
requirement for greater emissions offsets
for new or modified major stationary
sources under the state’s nonattainment
NSR program.5
1 73 FR 16436 (March 27, 2008), codified at 40
CFR 50.15.
2 CAA sections 107(d)(1) and 181(a)(1).
3 CAA section 181(a)(1).
4 CAA section 182(a).
5 CAA section 182(b).
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B. Background on the Chicago 2008
Ozone Nonattainment Area
On June 11, 2012,6 EPA designated
the Chicago area as a marginal
nonattainment area for the 2008 ozone
NAAQS. The Chicago area includes
Cook, DuPage, Kane, Lake, McHenry,
and Will Counties and part of Grundy
and Kendall Counties in Illinois; Lake
and Porter Counties in Indiana; and part
of Kenosha County in Wisconsin. On
May 4, 2016,7 pursuant to section
181(b)(2) of the CAA, EPA determined
that the Chicago area failed to attain the
2008 ozone NAAQS by the July 20,
2015, marginal area attainment deadline
and thus reclassified the area from
marginal to moderate nonattainment. In
that action, EPA established January 1,
2017, as the due date for the state to
submit all moderate area nonattainment
plan SIP requirements applicable to
newly reclassified areas.
In addition, effective March 6, 2017,
EPA found that 15 states and the District
of Columbia failed to submit SIP
revisions in a timely manner to satisfy
certain nonattainment plan
requirements for the 2008 ozone
NAAQS.8 This finding established
certain deadlines for the imposition of
sanctions if a state does not submit a
timely SIP revision addressing the
requirements for which EPA made the
finding and for EPA to promulgate a FIP
to address any outstanding SIP
requirements. As part of that action,
EPA made a finding that Indiana failed
to submit a SIP submission to meet the
marginal nonattainment NSR
requirements for the Indiana portion of
the Chicago area.
II. What is EPA’s evaluation of
Indiana’s submittal?
Indiana submitted a SIP revision
request on February 28, 2017, and
submitted supplemental information on
January 9, 2018, to address the moderate
area requirements for the Indiana
portion of the Chicago area for the 2008
ozone NAAQS. The submission
contained a number of nonattainment
plan elements, including a revised 2011
base year emissions inventory for VOC
and oxides of nitrogen (NOX), a 15%
RFP plan, a 3% RFP contingency
measure plan, 2017 VOC and NOX
motor vehicle emissions budgets, a
nonattainment NSR certification, a VOC
RACT certification, and an enhanced I/
M certification. The nonattainment NSR
certification included in the SIP
submission addresses the deficiency
that was the basis for the March 6, 2017,
6 77
FR 34221, effective July 20, 2012.
FR 26697.
8 82 FR 9158 (February 3, 2017).
7 81
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finding; therefore, approval of this SIP
revision would permanently stop the
sanctions and FIP clocks triggered by
EPA’s February 3, 2017 finding that
Indiana failed to submit a marginal
ozone nonattainment NSR plan. The
submission also included an attainment
demonstration, which will be addressed
in a separate action.
A. Revised 2011 Base Year Emissions
Inventory
CAA sections 172(c)(3) and 182(a)(1),
42 U.S.C. 7502(c)(3) and 7511a(a)(1),
require states to develop and submit, as
SIP revisions, comprehensive, accurate,
and complete emissions inventories for
all areas designated as nonattainment
for the ozone NAAQS. An emissions
inventory for ozone is an estimation of
actual emissions of VOC and NOX from
all sources located in the relevant
designated nonattainment area. For the
2008 ozone NAAQS, EPA has
recommended that states use 2011 as a
base year for the emissions estimates.9
On April 7, 2017,10 EPA approved the
2011 base year emissions inventory
submitted by the Indiana Department of
Environmental Management (IDEM) on
June 15, 2016, for the Indiana portion of
the Chicago area. IDEM included a
revised 2011 base year emissions
inventory in its February 27, 2017,
submission. The revised 2011 base year
emissions inventory only modifies the
emissions estimates for the on-road
mobile sector, with emissions estimates
43827
for point, area, and non-road mobile
sectors remaining unchanged from the
inventory approved by EPA.
In the original 2011 base year
emissions inventory approved by EPA,
Indiana derived 2011 onroad mobile
emissions by back-casting emissions
estimates generated by the MOVES2014
model for 2015 and 2020. The revised
onroad emissions estimates were
generated by running the MOVES2014
model for 2011. This is a more accurate
method for estimating 2011 onroad
emissions. Thus, EPA is proposing to
approve the 2011 base year emissions
inventory the state submitted with the
RFP plan as a revision to the Indiana
SIP.
TABLE 1—REVISED 2011 BASE YEAR EMISSIONS INVENTORY IN TONS PER SUMMER DAY
[tpsd]
VOC
NOX
Source sector
Lake County
Total
Lake County
Porter County
Total
EGU Point ................................................
Point .........................................................
Area ..........................................................
Non-road ..................................................
On-road ....................................................
0.44
15.39
12.54
7.55
6.92
0.19
1.68
5.53
6.64
2.66
0.63
17.07
18.07
14.19
9.58
24.62
43.10
5.80
8.07
17.85
5.53
23.36
3.89
4.62
6.85
30.15
66.46
9.69
12.69
24.70
Total ..................................................
42.84
16.70
59.54
99.44
44.25
143.69
B. 15% RFP Plan and 3% Contingency
Plan
1. Background
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Porter County
The CAA requires that states with
areas designated as nonattainment for
ozone achieve RFP toward attainment of
the ozone NAAQS. CAA section
172(c)(2) contains a general requirement
that nonattainment plans must provide
for emissions reductions that meet RFP.
For areas classified moderate and above,
section 182(b)(1) imposes a more
specific RFP requirement that a state
had to meet through a 15% reduction in
VOC emissions from the baseline
anthropogenic emissions within 6 years
after November 15, 1990. The state must
meet the 15% requirement by the end of
the 6-year period, regardless of when
the nonattainment area attains the
NAAQS. As with other nonattainment
plan requirements for more recent
iterations of the ozone NAAQS, EPA has
promulgated regulations and guidance
to interpret the statutory requirements
of the CAA.
9 78
FR 34178, 34190, (June 6, 2013).
FR 16934.
11 80 FR 12264. (March 6, 2015).
12 Ibid, at 12271 and 40 CFR 51.1110.
10 82
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EPA’s final rule to implement the
2008 ozone NAAQS (SIP Requirements
Rule),11 addressed, among other things,
the RFP requirements as they apply to
areas designated nonattainment and
classified as moderate for the 2008
ozone NAAQS.12 EPA interprets the
15% VOC emission reduction
requirement in CAA section 182(b)(1)
such that a state that has already met the
15% requirement for VOC for an area
under either the 1-hour ozone NAAQS
or the 1997 8-hour ozone NAAQS
would not have to fulfill that
requirement through reductions of VOC
again. Instead, EPA is interpreting CAA
section 172(c)(2) to require states with
such areas to obtain 15% ozone
precursor emission reductions (VOC
and/or NOX) over the first 6 years after
the baseline year for the 2008 ozone
NAAQS. The state previously met the
15% VOC reduction requirement of
CAA section 182(b)(1) for the Indiana
portion of the Chicago area under the 1hour ozone NAAQS. Therefore, the state
may rely upon both VOC and NOX
emissions reductions to meet the RFP
requirement for the 2008 ozone NAAQS.
EPA’s SIP Requirements Rule
indicates the base year for the 2008
ozone NAAQS, for which areas were
designated nonattainment effective July
20, 2012, can be 2011 or a different year
of the states choosing. However, states
selecting a pre-2011 alternate baseline
year must achieve 3% emission
reductions each year after the initial 6year period has concluded up to the
beginning of the attainment year. For a
multi-state area, states must agree on the
same base year. Wisconsin, Illinois, and
Indiana have selected the EPArecommended base year of 2011.13
States may not take credit for VOC or
NOX reductions occurring from sources
outside the nonattainment area for
purposes of meeting the 15% ROP and
3% RFP requirements of CAA sections
172(c)(2), 182(b)(1) and 182(c)(2)(B).
Indiana’s 15% RFP represents emissions
reductions which occurred in Indiana’s
portion of the nonattainment area from
13 On February 16, 2018, the D.C. Circuit Court
issued a decision in South Coast Air Quality
Management District v. EPA, 882 F.3d 1138 (D.C.
Cir. 2018), in which several parties challenged
different aspects of EPA’s SIP Requirements Rule
for the 2008 Ozone NAAQS. In this decision, the
Court upheld 2011 as a reasonable baseline year for
the 2008 ozone NAAQS but vacated the provision
allowing for an alternate year. Because Wisconsin,
Illinois, and Indiana have selected 2011 as the
baseline year, the decision does not impact
Indiana’s ROP plan.
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2011 to 2017, thereby satisfying this
requirement.
Except as specifically provided in
section 182(b)(1)(D) of the CAA, all state
control measures approved into the SIP
or Federal measures that provide
emissions reductions that occur after the
baseline emissions inventory year are
creditable for purposes of the RFP
requirements, provided that the
reductions meet the standard
requirements for creditability which
include being enforceable, quantifiable,
permanent, and surplus in terms of not
having previously been counted toward
RFP.
States must also include contingency
measures in their nonattainment plans.
The contingency measures required for
areas classified as moderate and above
under CAA sections 172(c)(9) and
182(c)(9) must provide for the
implementation of specific measures if
the area fails to attain or to meet any
applicable RFP milestone. The state
must submit these measures for
approval by EPA into the SIP as adopted
measures that would take effect without
further rulemaking action by the state or
the EPA upon a determination that an
area failed to attain or to meet the
applicable milestone. Per EPA guidance
for purposes of the ozone NAAQS,
contingency measures should represent
one year’s worth of RFP progress,
amounting to reductions of at least 3%
of the baseline emissions inventory for
the nonattainment area.14 The purpose
of the contingency measures is to
provide additional emission reductions
in the event of a failure to attain or meet
any applicable milestone, which would
occur while the state is revising its SIP
for the area to rectify the failure to attain
or to meet RFP requirements.15
Regarding the contingency measures,
EPA’s prior guidance for purposes of the
ozone NAAQS specifies that some
portion of the contingency measures
must include VOC reductions. This
previous limitation is no longer
necessary in all areas. In particular, EPA
has concluded that states with
nonattainment areas classified as
moderate and above that have already
completed the initial 15% VOC
reduction required by CAA section
182(b)(1)(A)(i), can meet the
contingency measures requirement
based entirely on NOX controls if that is
what the state’s analyses have
demonstrated would be most effective
in bringing the area into attainment.
There is no minimum VOC requirement.
Also, EPA is continuing its longstanding policy that allows states to use
promulgated Federal measures as
contingency measures as long as they
provide emission reductions in the
relevant years in excess of those needed
for attainment or RFP.16
2. Indiana’s 15% RFP and 3% RFP
Contingency Measures Plan
To demonstrate that the Indiana
portion of the Chicago area has achieved
15% RFP over the 6-year attainment
planning period, Indiana is using a 2011
base year inventory and a 2017 RFP
inventory. To develop the 2017
inventory, Indiana calculated on-road
emissions using EPA’s MOVES2014
model and non-road emissions using
EPA’s National Mobile Inventory Model
(NMIM). The MOVES model for the onroad sector and NMIM for the non-road
sector incorporate a number of Federal
emissions control programs into its
projections. These emissions reduction
measures are permanent and
enforceable and are implemented in the
nonattainment area. The MOVES and
NMIM models assumed increases in
vehicle or equipment population and
usage while projecting decreases in
ozone precursor emissions from 2011 to
2017. The estimated emissions
reductions are therefore not due to
reductions in source activity, but to the
implementation of control measures.
Tables 2 and 3 list the Federal
permanent and enforceable control
programs modeled by the MOVES
model for the on-road sector and NMIM
for the non-road sector, respectively.
TABLE 2—FEDERAL ON-ROAD EMISSION CONTROL PROGRAMS MODELED BY MOVES
On-road control program
Pollutants
Model year *
Regulation
Passenger vehicles, SUVs, and light duty trucks—emissions and fuel
standards.
Light-duty trucks and medium duty passenger vehicle—evaporative
standards.
Heavy-duty highway compression engines ..........................................
Heavy-duty spark ignition engines ........................................................
Motorcycles ...........................................................................................
Mobile Source Air Toxics—fuel formulation, passenger vehicle emissions, and portable container emissions.
Light duty vehicle corporate average fuel economy standards ............
VOC & NOX ................
40 CFR parts 85 & 86.
VOC ............................
2004–09+ (Tier 2)
2017+ (Tier 3).
2004–10 .....................
VOC & NOX ................
VOC & NOX ................
VOC & NOX ................
Organic Toxics & VOC
2007+ .........................
2005–08+ ...................
2006–10 (Tier 1 & 2) ..
2009–15 ** ..................
Fuel efficiency (VOC &
NOX).
2012–16 & 2017–25 ...
40 CFR part 86.
40 CFR part 86.
40 CFR part 86.
40 CFR part 86.
40 CFR parts 59, 80,
85, & 86.
40 CFR part 600.
* The range in model years affected can reflect phasing of requirements based on engine size or initial years for replacing earlier tier requirements.
** The range in model years reflects phased implementation of fuel, passenger vehicle, and portable container emission requirements as well
as the phasing by vehicle size and type.
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TABLE 3—FEDERAL NON-ROAD EMISSION CONTROL PROGRAMS MODELED BY NMIM
Nonroad control program *
Pollutants
Model year **
Compression Ignition ............................................................................
VOC & NOX ................
2000–2015+ (Tier 4) ..
Large Spark Ignition ..............................................................................
Marine Spark Ignition ............................................................................
Recreational Vehicle .............................................................................
Small Spark Ignition Engine <19 Kw—emission standards .................
VOC
VOC
VOC
VOC
2007+ .........................
2010+ .........................
2006–2012 (Tiers 1–3)
2005–2012 (Tiers 2 &
3).
14 See the March 6, 2015 SIP Requirements Rule
(80 FR 12264 at 12285) and April 16, 1992 General
Preamble section III.A.3.c (57 FR 13498 at 13511).
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15 80
16 80
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&
&
&
&
NOX
NOX
NOX
NOX
................
................
................
................
FR 12264 at 12285.
FR 12264 at 12285.
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Regulation
40 CFR
1039.
40 CFR
40 CFR
40 CFR
40 CFR
1054.
parts 89 &
part 1048.
part 1045.
part 1051.
parts 90 &
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TABLE 3—FEDERAL NON-ROAD EMISSION CONTROL PROGRAMS MODELED BY NMIM—Continued
Nonroad control program *
Pollutants
Model year **
Regulation
Small Spark Ignition Engine <19 Kw—evaporative standards .............
VOC ............................
2008–2016 .................
40 CFR parts 1045,
54, & 60.
* Compression ignition applies to diesel non-road compression engines including engines operated in construction, agricultural, and mining
equipment. Recreational vehicles include snowmobiles, off-road motorcycles, and all-terrain vehicles. Small spark ignition engines include engines operated in lawn and hand-held equipment.
** The range in model years affected can reflect phasing of requirements based on engine size or initial years for replacing earlier tier
requirements.
Indiana used the 2017 EPA-projected
National Emissions Inventory (NEI) to
obtain estimated point and area source
emissions. While EPA projected point
and area source emissions to decrease
between 2011 and 2017, Indiana did not
document the control programs and
associated reductions in emissions for
these sectors or determine to what
extent any reduction may be attributed
to reductions in source activity.
Therefore, Indiana took no credit for
emissions reductions from these source
sectors in its RFP or RFP contingency
measures calculations. Table 4 shows
Indiana’s 2017 projected emissions
inventory. Table 5 shows Indiana’s 2017
RFP and RFP contingency emissions
inventory, which assumes no reduction
in emissions between 2011 and 2017
from the point and area source sectors.
TABLE 4—PROJECTED 2017 EMISSIONS INVENTORY
[tpsd]
VOC
NOX
Source sector
Lake County
Porter County
Total
Lake County
Porter County
Total
EGU Point ................................................
Non-EGU Point ........................................
Area ..........................................................
Non-road ..................................................
On-road ....................................................
0.09
15.34
11.73
5.03
4.33
0.07
1.67
5.08
4.44
1.63
0.16
17.01
16.81
9.47
5.96
4.07
42.44
5.10
5.59
10.15
1.36
23.10
3.25
3.48
4.35
5.43
65.54
8.35
9.07
14.50
Total ..................................................
36.52
12.89
49.41
67.35
35.54
102.90
TABLE 5—2017 RFP AND RFP CONTINGENCY MEASURES EMISSIONS INVENTORY
[tpsd]
VOC
NOX
Source sector
Lake County
Porter County
Total
Lake County
Porter County
Total
EGU Point ................................................
Non-EGU Point ........................................
Area ..........................................................
Non-road ..................................................
On-road ....................................................
0.44
15.39
12.54
5.03
4.33
0.19
1.68
5.53
4.44
1.63
0.63
17.07
18.07
9.47
5.96
24.62
43.10
5.80
5.59
10.15
5.53
23.36
3.89
3.48
4.35
30.15
66.46
9.69
9.07
14.50
Total ..................................................
37.73
13.47
51.20
89.26
40.61
129.87
Indiana submitted documentation
showing that emission reductions in the
Indiana portion of the Chicago area met
the 15% RFP and 3% RFP contingency
measures requirements entirely through
Federal permanent and enforceable
control measures within the mobile
source sectors. Table 6 shows the
calculations Indiana used to determine
that the mobile source emissions
reductions meet the RFP and RFP
contingency measures requirements.
TABLE 6—2017 RFP AND CONTINGENCY TARGET LEVEL CALCULATIONS
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[emissions in tpsd]
Description
Formula
VOC
NOX
A. 2011 RFP Base Year Inventory ..............................................................................................
B. RFP Reductions totaling 15% .................................................................................................
C. RFP Emissions Reductions Required Between 2011 & 2017 ...............................................
D. RFP Target Level for 2017 .....................................................................................................
E. Contingency Percentage .........................................................................................................
F. Contingency Emission Reduction Requirements ....................................................................
G. RFP + Contingency Target Level ...........................................................................................
H. 2017 Projected Emissions (2017 RFP & Contingency Inventory) .........................................
I. Compare RFP & Contingency Target with 2017 Projected Emissions to determine if RFP
and Contingency Measure Requirements Are Met .................................................................
........................
........................
A*B
A¥C
........................
A*E
A¥C¥F
........................
59.54
9%
5.36
54.18
2%
1.2
52.99
51.20
143.69
6%
8.62
135.07
1%
1.44
133.63
129.87
H2014
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TABLE 6—2017 RFP AND CONTINGENCY TARGET LEVEL CALCULATIONS—Continued
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[emissions in tpsd]
Description
Formula
VOC
NOX
J. Total Surplus Reductions ........................................................................................................
G¥H
1.79
3.76
Indiana has demonstrated that
emission reductions attributable to
permanent and enforceable measures
will result in at least an 18% reduction
(15% for RFP and 3% for contingency
measure requirements) in the Indiana
portion of the Chicago area over the 6year attainment planning time period,
starting with the 2011 base year. Thus,
EPA is proposing to approve Indiana’s
15% RFP and 3% contingency measure
plan for the Indiana portion of the
Chicago area for the 2008 ozone
standard.
EPA notes that the control measures
Indiana is relying upon to meet the RFP
contingency measures requirement are
already implemented. Contingency
measures may include Federal measures
and local measures already scheduled
for implementation, as long as the
resulting emission reductions are in
excess of those needed for attainment or
to meet other nonattainment plan
requirements. EPA interprets the CAA
not to preclude a state from
implementing such measures before
they are triggered by a failure to meet
RFP or failure to attain. For more
information on contingency measures,
see the General Preamble (57 FR 13510)
and the 2008 Ozone Implementation
Rule (80 FR 12264, 12285).
The appropriateness of relying on
already-implemented control measures
to meet the contingency measures
requirement has been addressed in two
Federal circuit court decisions. See
Louisiana Environmental Action
Network (LEAN) v. EPA, 382 F.3d 575,
586 (5th Cir. 2004), Bahr v. United
States EPA, 836 F.3d 1218 (9th Cir.
2016), cert. denied, 199 L. Ed. 2d 525,
2018 U.S. LEXIS 58 (Jan. 8, 2018). EPA
believes that the language of section
172(c)(9) and 182(c)(9) is ambiguous
with respect to this issue, and that it is
reasonable for the agency to interpret
the statutory language to allow approval
of already implemented measures as
contingency measures, so long as they
meet other parameters such as providing
excess emissions reductions that the
state has not relied upon to meet other
nonattainment plan requirements or in
the modeled attainment demonstration
in the nonattainment plan for the
NAAQS at issue. Until the Bahr
decision, under EPA’s longstanding
interpretation of CAA section 172(c)(9)
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and 182(c)(9), states could rely on
control measures that were already
implemented (so called ‘‘early
triggered’’ contingency measures) as a
valid means to meet the Act’s
contingency measures requirement. The
Ninth Circuit decision in Bahr leaves a
split among the Federal circuit courts,
with the Fifth Circuit upholding the
Agency’s interpretation of section
172(c)(9) to allow early triggered
contingency measures and the Ninth
Circuit rejecting that interpretation. The
Seventh Circuit in which Indiana is
located has not addressed the issue, nor
has the Supreme Court or any other
circuit court other than the Fifth and
Ninth.
Because there is a split in the Federal
circuits on this issue, EPA expects that
states located in circuits other than the
Ninth may elect to rely on EPA’s
longstanding interpretation of section
172(c)(9) allowing early triggered
measures to be approved as contingency
measures, in appropriate circumstances.
EPA’s revised Regional Consistency
regulations pertaining to SIP provisions
authorize the Agency to follow this
interpretation of section 172(c)(9) in
circuits other than the Ninth. See 40
CFR part 56. To ensure that early
triggered contingency measures
appropriately satisfy all other relevant
CAA requirements, EPA will carefully
review each such measure, and intends
to consult with states considering such
measures early in the attainment plan
development process.
As shown above, the emissions
reductions projected through 2018 are
sufficient to meet the requirements for
RFP contingency measures, consistent
with EPA’s interpretation of the CAA to
allow approval of already implemented
control measures as contingency
measures in states outside the Ninth
Circuit. Therefore, we propose approval
of the contingency measures submitted
by the state in the nonattainment plan
for the Wisconsin portion of the Chicago
area.
C. 2017 Motor Vehicle Emissions
Budgets (MVEBs)
Under section 176(c) of the CAA, new
transportation plans, programs, or
projects that receive Federal funding or
support, such as the construction of new
highways, must ‘‘conform’’ to (i.e., be
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consistent with) the SIP. Conformity to
the SIP means that transportation
activities will not cause new air quality
violations, worsen existing air quality
problems, or delay timely attainment of
the NAAQS or interim air quality
milestones. Regulations at 40 CFR part
93 set forth EPA policy, criteria, and
procedures for demonstrating and
assuring conformity of transportation
activities to a SIP.
Under the CAA, states are required to
submit, at various times, control strategy
plans for nonattainment areas and
maintenance plans for areas seeking
redesignations to attainment of the
ozone standard and maintenance
areas.17 These control strategy plans
(including reasonable further progress
plans and attainment plans for purposes
of the ozone NAAQS) and maintenance
plans must include MVEBs for the
relevant criteria pollutant or its
precursor pollutants (VOC and NOX for
ozone) to address pollution from onroad transportation sources. The MVEBs
are the portion of the total allowable
emissions that are allocated to highway
and transit vehicle use that, together
with emissions from other sources in
the area, will meet an RFP milestone or
provide for attainment or maintenance
of the NAAQS.18 The MVEB serves as a
ceiling on emissions from an area’s
planned transportation system.19
When reviewing control strategy or
maintenance plan submissions, EPA
must affirmatively find that the MVEBs
contained therein are adequate for use
in determining transportation
conformity. Once EPA affirmatively
finds that the submitted MVEBs are
adequate for transportation purposes,
the MVEBs must be used by state and
Federal agencies in determining
whether proposed transportation
projects conform to the SIP as required
by section 176(c) of the CAA.
EPA’s substantive criteria for
determining adequacy of a MVEB are set
out in 40 CFR 93.118(e)(4). The process
17 See the SIP requirements for the 2008 ozone
standard in EPA’s March 6, 2015 implementation
rule (80 FR 12264).
18 40 CFR 93.101.
19 The MVEB concept is further explained in the
preamble to the November 24, 1993, Transportation
Conformity Rule (58 FR 62188). The preamble also
describes how to establish the MVEB in the SIP and
how to revise the MVEB, if needed, subsequent to
initially establishing a MVEB in the SIP.
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for determining adequacy consists of
three basic steps: Public notification of
a SIP submission; provision for a public
comment period; and EPA’s adequacy
determination. This process for
determining the adequacy of submitted
MVEBs for transportation conformity
purposes was initially outlined in EPA’s
May 14, 1999 guidance, ‘‘Conformity
Guidance on Implementation of March
2, 1999, Conformity Court Decision.’’
EPA adopted regulations to codify the
adequacy process in the Transportation
Conformity Rule Amendments for the
‘‘New 8-Hour Ozone and PM2.5 National
Ambient Air Quality Standards and
Miscellaneous Revisions for Existing
Areas; Transportation Conformity Rule
Amendments—Response to Court
Decision and Additional Rule Change,’’
on July 1, 2004.20 Additional
information on the adequacy process for
transportation conformity purposes is
available in a June 30, 2003, proposed
rule titled, ‘‘Transportation Conformity
Rule Amendments: Response to Court
Decision and Additional Rule
Changes.’’ 21
Indiana’s RFP and contingency
measure plan includes VOC and NOX
MVEBs for the Indiana portion of the
Chicago area for 2017. EPA reviewed the
VOC and NOX MVEBs through the
adequacy process. Indiana’s February
28, 2017, RFP and contingency measure
SIP submission (as supplemented on
January 9, 2018), including the VOC and
NOX MVEBs for the Indiana portion of
the Chicago area, was available for
public comment on EPA’s adequacy
website on February 2, 2018, found at:
https://www.epa.gov/otaq/
stateresources/transconf/currsips.htm.
The EPA public comment period on
adequacy of the 2017 MVEBs for the
Indiana portion of the Chicago area
closed on March 5, 2018. No comments
on the submittal were received during
the adequacy comment period. The
submitted RFP and contingency
measure plan, which included the
MVEBs, was endorsed by the Governor’s
designee and was subject to a state
public hearing. The MVEBs were
developed as part of an interagency
consultation process which includes
Federal, state, and local agencies. The
MVEBs were clearly identified and
precisely quantified. These MVEBs,
when considered together with all other
emissions sources, are consistent with
the 15% RFP and 3% RFP contingency
measures requirements of the 2008 8hour ozone standard.
TABLE 7—2017 VOC AND NOX MVEBS FOR THE INDIANA PORTION OF THE CHICAGO AREA
[tpsd]
2017
On-road emissions
VOC .................................................
NOX ..................................................
5.96
14.50
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As shown in Table 7, the 2017 MVEBs
exceed the estimated 2017 on-road
sector emissions. In an effort to
accommodate future variations in travel
demand models and vehicle miles
traveled forecast, Indiana allocated a
portion of the surplus RFP and
contingency plan reductions to the
mobile sector. Indiana has demonstrated
that the Indiana portion of the Chicago
area can meet the 15% RFP and 3% RFP
contingency measure requirements of
the 2008 ozone NAAQS with mobile
source emissions of 6.85 tpsd of VOC
and 16.68 tpsd of NOX in 2017, because
despite partial allocation of the RFP and
RFP contingency measures plan surplus
reductions, emissions will remain under
2017 RFP plus contingency measure
target levels. EPA has found adequate
and is thus proposing to approve the
2017 VOC and NOX MVEBs for use to
determine transportation conformity in
the Indiana portion of the Chicago area
under the 2008 ozone NAAQS because
EPA has determined that the area can
20 69
21 68
FR 40004.
FR 38974, 38984.
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RFP +
Contingency plan
surplus reductions
Allocation of
surplus reductions
to on-road mobile
sector
1.79
3.65
0.89
2.18
2017 MVEBs
6.85
16.68
Sections 172(c)(1) and 182(b)(2) of the
CAA require states to implement RACT
in ozone nonattainment areas classified
as moderate (and higher). Specifically,
these areas are required to implement
RACT for all major VOC and NOX
emissions sources and for all sources
covered by a Control Techniques
Guideline (CTG). A CTG is a document
issued by EPA which establishes a
‘‘presumptive norm’’ for RACT for a
specific VOC source category. States
must submit rules, or negative
declarations when no such sources exist
for CTG source categories.
EPA’s SIP Requirements Rule for the
2008 ozone NAAQS indicates that states
may meet RACT through the
establishment of new or more stringent
requirements that meet RACT control
levels, through a certification that
previously adopted RACT controls in
their SIPs approved by EPA for a prior
ozone NAAQS also represent adequate
RACT control levels for attainment of
the 2008 ozone NAAQS, or with a
combination of these two approaches. In
addition, a state must submit a negative
declaration in instances where there are
no CTG sources.
In its February 28, 2017 submission,
Indiana certified that the existing VOC
rules contained in 326 Indiana
Administrative Code (IAC) 8 satisfy the
VOC RACT requirements of Section
182(b)(2) of the CAA and have been
approved into the SIP by EPA. Indiana
also certified that the negative
declaration approved into the SIP by
EPA for the fiberglass boat
manufacturing materials CTG is still
current.22 Table 8 lists these state
regulations and identifies the associated
SIP approvals by EPA.
22 The NEI, the Harris Manufacturing Directory
and the Manta small business directory were
reviewed to spot check the validity of the
previously approved negative declaration for this
category. No fiberglass boat manufacturing facilities
subject to the CTG were identified.
meet the 15% RFP and 3% RFP
contingency measure requirements of
the 2008 ozone NAAQS with mobile
source emissions at the levels of the
MVEBs.
D. VOC RACT Certification
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TABLE 8—VOC RACT REGULATIONS APPROVED INTO THE INDIANA SIP
CTGs and ACTs 1
Applicable Indiana
regulation
EPA 453/R–08–004 2008/09—Control Techniques Guidelines for Fiberglass Boat Manufacturing Materials.
EPA 453/R–08–006, 2008/09—Control Techniques Guidelines for
Automobile and Light-Duty Truck Assembly Coatings and EPA 453/
R–08–002, 2008/09—Protocol for Determining the Daily Volatile Organic Compound Emission Rate of Automobile and Light-Duty Truck
Primer-Surfacer and Topcoat Operations.
EPA 453/R–07–003, 2007/09—Control Techniques Guidelines for
Paper, Film, and Foil Coatings.
EPA 453/R–07–005, 2007/09—Control Techniques Guidelines for
Metal Furniture Coatings.
EPA 453/R–07–004, 2007/09—Control Techniques Guidelines for
Large Appliance Coatings.
EPA 453/R–08–003, 2008/09—Control Techniques Guidelines for Miscellaneous Metal and Plastic Parts Coatings.
Negative Declaration Letter—06/
05/2009.
326 IAC 8–2–2—Automobile and
Light Duty Truck Coating Operations.
EPA–453/R–06–004 2006/09—Control Techniques Guidelines for Flat
Wood Paneling Coatings.
EPA–453/R–06–003 2006/09—Control Techniques Guidelines for
Flexible Package Printing.
Non-CTG .................................................................................................
EPA–453/R–06–002 2006/09—Control Techniques Guidelines for Offset Lithographic Printing and Letterpress Printing.
EPA–453/R–06–001, 2006/09—Control Techniques Guidelines for Industrial Cleaning Solvents.
EPA–450/3–84–015 1984/12—Control of Volatile Organic Compound
Emissions from Air Oxidation Processes in Synthetic Organic Chemical Manufacturing Industry and EPA–450/4–91–031 1993/08—Control of Volatile Organic Compound Emissions from Reactor Processes and Distillation Operations in Synthetic Organic Chemical
Manufacturing Industry.
EPA–453/R–93–020, 1994/02—Control of Volatile Organic Compound
Emissions from Batch Processes ACT (Note—also released as
EPA–453/R–93–017).
EPA–453/D–93–056, 1992/09—Control of Volatile Organic Compound
Emissions from Industrial Wastewater CTG (draft).
Note—CTG not finalized but issued as ACT in 1994. ............................
(No Report ID) 1994/04 Industrial Wastewater Alternative Control
Technology..
Note—ACT consists of cover memo with option tables + CTG (draft)
EPA–453/D-93–056..
59 FR–29216, 6/06/94—1994/06 Aerospace MACT and EPA–453/R–
97–004, 1997/12 Aerospace (CTG & MACT).
EPA 453/R–08–005, 2008/09—Control Techniques Guidelines for Miscellaneous Industrial Adhesives.
daltland on DSKBBV9HB2PROD with PROPOSALS
1 ACTs
EPA approval into the SIP
326 IAC 8–2–5—Paper Coating
Operations.
326 IAC 8–2–6—Metal Furniture
Coating Operations.
326 IAC 8–2–7—Large Appliance
Coating Operations.
326 IAC 8–2–9—Miscellaneous
Metal and Plastic Parts Coating
Operations.
326 IAC 8–2–10—Flat Wood Panels; Manufacturing Operations.
326 IAC 8–5–5—Graphic Arts and
Graphic Arts Operations.
IAC 326 8–7—Specific VOC Reduction Requirements for Lake,
Porter, Clark, and Floyd Counties.
326 IAC 8–16—Offset Lithographic
Printing and Letterpress Printing.
326 IAC 8–17—Industrial Solvent
Cleaning Operations.
326 IAC 8–18—Synthetic Organic
Chemical Manufacturing Industry Air Oxidation, Distillation, and
Reactor Processes.
75 FR 8246 (02/24/2010).
75 FR 8246 (02/24/2010) Revision: 76 FR 63549 (10/13/2011).
75 FR 8246 (02/24/2010).
63 FR 35141 (06/29/1998) and 75
FR 8246 (02/24/2010).
60 FR 34856 (07/05/1995).
75 FR 8246 (02/24/2010).
326 IAC 8–19—Control of Volatile
Organic Compound Emissions
from Process Vents in Batch
Operations.
326 IAC 8–20—Industrial Wastewater.
326 IAC 8–21—Aerospace Manufacturing and Rework Operations.
326 IAC 8–22—Miscellaneous Industrial Adhesives.
describe available control technologies and their respective cost effectiveness but do not establish presumptive RACT.
EPA has reviewed Indiana’s
certification that it has adopted VOC
control regulations for stationary
sources that constitute RACT, and
determined that the set of regulations
cited by the state and negative
declaration for fiberglass boat
manufacturing constitute RACT for
purposes of the 2008 ozone NAAQS in
this nonattainment area. Therefore, EPA
is proposing to approve the state’s
submission as meeting the VOC RACT
requirements for the Indiana portion of
the Chicago area for the 2008 ozone
NAAQS.
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E. Motor Vehicle I/M Program
Certification
The requirement to adopt a motor
vehicle I/M program for moderate ozone
nonattainment areas is described in
CAA section 182(b)(4), and the
regulations for basic and enhanced I/M
programs are found at 40 CFR part 51,
subpart S. Under these cumulative
requirements, states with areas
classified as moderate nonattainment for
ozone with 1990 Census-defined
urbanized populations of 200,000 or
more are required to adopt basic I/M
programs, while serious and higher
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classified ozone nonattainment areas
outside of the northeast ozone transport
region with 1980 Census-defined
urbanized populations of 200,000 or
more are required to adopt enhanced I/
M programs. The Chicago area meets the
criteria for mandatory I/M under the
2008 ozone NAAQS.
The Indiana portion of the Chicago
area was required to adopt an enhanced
I/M program under the 1-hour ozone
NAAQS. EPA approved Indiana’s
enhanced I/M program on March 19,
1996 (61 FR 11142). Indiana’s I/M
program is authorized by state statute
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Indiana Code (IC) 13–17–5, paid
through the general funds, and
implemented through rules promulgated
by the Indiana Environmental Rules
Board at 326 IAC 13. These
requirements remain in place in
Indiana’s ozone SIP. In its February 28,
2017, submission, Indiana certified that
the existing enhanced I/M program
continues to satisfy the I/M
requirements of the CAA for the Indiana
portion of the Chicago area. Therefore,
EPA is proposing to find that Indiana
has met the I/M requirement for its
portion of the Chicago area for the 2008
ozone NAAQS.
F. Nonattainment New Source Review
1. Background
CAA sections 110(a)(2) and 172(c)(5)
require permits for the construction of
new or modified major stationary
sources anywhere in a nonattainment
area in accordance with CAA section
173. CAA section 182 contains
additional requirements applicable to
ozone nonattainment areas.
Nonattainment NSR requirements are
codified at 40 CFR 51.165.
On March 6, 2017, EPA found that
Indiana failed to submit marginal ozone
nonattainment NSR rules for the Indiana
portions of the Chicago area and
Cincinnati 23 2008 ozone nonattainment
areas.24 On February 28, 2017, Indiana
submitted its nonattainment NSR
43833
certification to address nonattainment
NSR requirements for marginal and
moderate ozone nonattainment areas.25
Indiana has certified that specific
sections of its nonattainment NSR rules
at 326 IAC 2–3 continue to meet the
nonattainment NSR program
requirements for ozone nonattainment
areas under the 2008 ozone NAAQS.
Table 9 provides the sections of
Indiana’s nonattainment NSR rule
corresponding to the relevant
requirements at 40 CFR 51.165. 326 IAC
2–3 was originally approved into the
SIP effective December 6, 1994,26 with
revisions subsequently approved into
the SIP effective September 6, 2011.27
Each requirement identified in Indiana’s
certification has been unchanged since
EPA last approved it.
TABLE 9—NONATTAINMENT NSR RULES INDIANA CERTIFIED AS MEETING FEDERAL RULES
Federal rule
40
40
40
40
40
40
40
40
CFR
CFR
CFR
CFR
CFR
CFR
CFR
CFR
51.165(a)(1)(iv)(A)(1)(i)–(iii) ..........................................................................................
51.165(a)(1)(iv)(A)(2) ....................................................................................................
51.165(a)(1)(iv)(A)(3) ....................................................................................................
51.165(a)(1)(v)(E) .........................................................................................................
51.165(a)(1)(x)(A)–(C) ..................................................................................................
51.165(a)(3)(ii)(C)(1)–(2) ...............................................................................................
51.165(a)(8) ..................................................................................................................
51.165(a)(9)(ii)-(iv) ........................................................................................................
For the following reasons, we are
proposing to approve Indiana’s
certification that 326 IAC 2–3 is
consistent with 40 CFR 51.165 and
meets the requirements of CAA sections
172(c)(5), 173, 110(a)(2), 182(a)(4), and
182(b)(5) under the 2008 ozone standard
for the Indiana portion of the Chicago
area ozone nonattainment area.
Approval of Indiana’s nonattainment
NSR certification would address the
deficiency that was the basis for the
March 6, 2017 finding. Therefore, final
approval of this SIP revision will
permanently stop the sanctions and FIP
clocks triggered by EPA’s February 3,
2017 finding that Indiana failed to
submit a marginal ozone nonattainment
NSR plan.
2. Extreme Ozone Nonattainment Area
and Ozone Transport Region
Nonattainment NSR Requirements
In its February 28, 2017 submission,
Indiana states that its nonattainment
NSR rules do not include extreme ozone
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Indiana rule
23 The Cincinnati, Ohio-Kentucky-Indiana 8-hour
ozone nonattainment area has since been
redesignated to attainment effective April 7, 2017.
See 82 FR 16940.
24 See 82 FR 9158.
25 The Chicago-Naperville 2008 8-hour ozone
nonattainment area was reclassified to moderate
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326
326
326
326
326
326
326
326
IAC
IAC
IAC
IAC
IAC
IAC
IAC
IAC
2–3–1(z)(1) and (2).
2–3–1(z)(1) and (2).
2–3–1(z)(5).
2–3–1(y)(1).
2–3–1(pp).
2–3–3(b)(5).
2–3–1(y); 326 IAC 2–3–2(a) and (b).
2–3–3(a)(5)(B).
nonattainment requirements because
Indiana has never had an extreme ozone
nonattainment area. We concur with the
statement that Indiana has never had an
extreme ozone nonattainment area.
Further, the finding of failure to submit
applies to marginal ozone
nonattainment NSR requirements, not
extreme. Finally, the Chicago area ozone
nonattainment area was reclassified to a
moderate ozone nonattainment area
which requires moderate, not extreme,
ozone nonattainment NSR requirements.
For these reasons, Indiana’s
nonattainment NSR program does not
require extreme ozone nonattainment
requirements at this time. The following
extreme ozone nonattainment NSR
requirements are not included as part of
Indiana’s nonattainment NSR rules: 40
CFR 51.165(a)(1)(iv)(A)(1)(iv), 40 CFR
51.165(a)(1)(iv)(A)(2)(vi), 40 CFR
51.165(a)(1)(v)(F), 40 CFR
51.165(a)(1)(x)(E), and 40 CFR
51.165(a)(9)(ii)(E).
Indiana’s submission does not address
ozone transport region requirements.
However, no portion of Indiana is
currently part of an ozone transport
region; therefore, ozone transport region
nonattainment NSR requirements do not
apply in Indiana. The following ozone
transport region nonattainment NSR
requirements are not included as part of
Indiana’s nonattainment NSR rules: 40
CFR 51.165(a)(1)(iv)(A)(1)(ii), 40 CFR
51.165(a)(1)(iv)(A)(2)(ii), 40 CFR
51.165(a)(1)(iv)(A)(2)(ii), 40 CFR
51.165(a)(1)(v)(E), 40 CFR
51.165(a)(1)(x)(C), 40 CFR 51.165(a)(8),
and 40 CFR 51.165(a)(9)(iii).
Extreme ozone nonattainment area
and ozone transport region
nonattainment NSR requirements will
not be addressed further in this analysis
of Indiana’s ozone nonattainment NSR
program certification because they do
not apply to Indiana at this time. If, in
the future, Indiana has an extreme
ozone nonattainment area or becomes
part of an ozone transport region, then
nonattainment effective June 3, 2017. See 81 FR
26697.
26 See 59 FR 51108. In its submittal, Indiana cites
94 FR 24838 as the initial approval for each
requirement. The Federal Register Document
Number of the initial approval is 94–24838 and
corresponds to the proposed Approval and
Promulgation of a New Source Review
Implementation Plan; Indiana. Federal Register
Document Number 94–24837 is the direct final
Approval and Promulgation of a New Source
Review Implementation Plan; Indiana. The direct
final rule can be found at 59 FR 51108. Throughout
today’s proposed rule, the direct final approval of
Indiana’s NSR program will be cited as 59 FR
51108.
27 See 76 FR 40242.
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Indiana’s SIP would need to be revised
to establish the appropriate
nonattainment NSR requirements.
3. 40 CFR 51.165(a)(1)(iv)(A)(1)(i)–(iv)
and (2)—Major Source Thresholds for
Ozone
40 CFR 51.165(a)(1)(iv)(A)(1)(i)–(iv)
and (2) defines the major source
thresholds for the ozone precursors VOC
and NOX. The major source threshold
for both VOC and NOX vary depending
on the classification of the ozone
nonattainment area. For marginal and
moderate ozone nonattainment areas, a
major stationary source of ozone is a
source that emits, or has the potential to
emit, 100 tons per year or more of VOC
or NOX. Different emissions thresholds
apply for serious, severe, and extreme
ozone nonattainment areas and areas in
an ozone transport region.
326 IAC 2–3–1(z)(1) generally defines
a major stationary source as a stationary
source that emits, or has the potential to
emit, 100 tons per year or more of any
regulated NSR pollutant, with an
exception for ozone provided in 326
IAC 2–3–1(z)(2). 326 IAC 2–3–1(z)(2)
defines a major stationary source for
ozone nonattainment areas, specifying
that the major source threshold is 100
tons per year or more of VOC or NOX
in marginal and moderate ozone
nonattainment areas. 326 IAC 2–3–
1(z)(1) and (2) remain consistent with 40
CFR 51.165(a)(1)(iv)(A)(1)(i)–(iv) and (2)
for marginal and moderate ozone
nonattainment areas.
4. 40 CFR 51.165(a)(1)(iv)(A)(3)—
Change Constitutes Major Source by
Itself
40 CFR 51.165(a)(1)(iv)(A)(3) requires
any physical change that would
constitute a major stationary source by
itself to be treated as a major stationary
source if the stationary source does not
qualify as a major stationary source. 326
IAC 2–3–1(z)(5) requires the same and
remains consistent with 40 CFR
51.165(a)(1)(iv)(A)(3).
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5. 40 CFR 51.165(a)(1)(v)(E)—Significant
Net Emissions Increase of NOX is
Significant for Ozone
40 CFR 51.165(a)(1)(v)(E) requires
significant net emissions increases of
NOX to be considered significant for
ozone. For major modifications, 326 IAC
2–3–1(y)(1) requires significant net
emissions increases of NOX to be
considered significant for ozone in
ozone nonattainment areas. 326 IAC 2–
3–1(y)(1) exempts NOX when the
Administrator has granted a NOX waiver
pursuant to CAA section 182(f) and 40
CFR 51.165(a)(8). As a result, 326 IAC
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2–3–1(y)(1) remains consistent with 40
CFR 51.165(a)(1)(v)(E).
6. 40 CFR 51.165(a)(1)(x)(A)–(C)—
Significant Emission Rates for VOC and
NOX as Ozone Precursors
40 CFR 51.165(a)(1)(x)(A) defines the
significant emission rate for ozone as 40
tons per year of VOC or NOX. 326 IAC
2–3–1(pp) defines the significant
emission rate for ozone in marginal and
moderate nonattainment areas as 40
tons per year of VOC or NOX (unless a
NOX waiver is in effect). 326 IAC 2–3–
1(pp) remains consistent with 40 CFR
51.165(a)(1)(x)(A) for marginal and
moderate ozone nonattainment areas.
40 CFR 51.165(a)(1)(x)(B) and (C)
define the significant emission rate for
ozone in serious or severe
nonattainment areas as 25 tons per year
of VOC or NOX. For the purpose of
implementing nonattainment NSR in
marginal and moderate ozone
nonattainment areas, serious and severe
ozone significant emission rates are not
required.
7. 40 CFR 51.165(a)(3)(ii)(C)(1)–(2)—
Provisions for Emissions Reduction
Credits
40 CFR 51.165(a)(3)(ii)(C)(1) and (2)
are the requirements that make emission
reductions achieved by shutting down
an existing emission unit or curtailing
production or operating hours
creditable. Such reductions must be
surplus, permanent, quantifiable, and
federally enforceable. Shutdowns or
curtailments must have occurred after
the last day of the base year for the SIP
planning process. Reviewing authorities
may choose to consider a prior
shutdown or curtailment to have
occurred after the last day of the base
year if the projected emissions
inventory used to develop the
attainment demonstration explicitly
includes emissions from the previously
shutdown or curtailed emissions units,
but in no event may credit be granted
for shutdowns that occurred prior to
August 7, 1977. Shutdown or
curtailment reductions occurring before
the last day of the base year for the SIP
planning process may also be generally
credited if the shutdown or curtailment
occurred on or after the date the
construction permit application is filed
or if the applicant can establish that the
proposed new emissions unit is a
replacement for the shutdown or
curtailed emission unit and the
emission reductions that result are
surplus, permanent, quantifiable, and
federally enforceable. 326 IAC 2–3–
3(b)(5) remains consistent with 40 CFR
51.165(a)(3)(ii)(C)(1)(i) and 40 CFR
51.165(a)(3)(ii)(C)(2)(ii).
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326 IAC 2–3–3(b)(5)(A) credits
emission reductions from emission unit
shutdowns and curtailments if they
occurred on or after the date of the most
recent emissions inventory or
attainment demonstration. Prior
shutdown or curtailment emission
reductions may be considered to have
occurred after the date of the most
recent emissions inventory if the
inventory explicitly includes the
emissions from the previously
shutdown or curtailed emissions units.
326 IAC 2–3–3(b)(5)(A) remains
consistent with 40 CFR
51.165(a)(3)(ii)(C)(1)(ii).
326 IAC 2–3–3(b)(5)(B) allows
reductions to be credited absent an
approved attainment demonstration if
the shutdown or curtailment occurred
on or after the date the new source
permit application is filed or if the
applicant can establish that the
proposed new source is a replacement
for the shutdown or curtailed emissions
unit, with the exception of shutdowns
occurring prior to August 7, 1977. 326
IAC 2–3–3(b)(5)(B) remains consistent
with 40 CFR 51.165(a)(3)(ii)(C)(2)(ii).
8. 40 CFR 51.165(a)(8)—Requirements
for VOC Apply to NOX as Ozone
Precursors
40 CFR 51.165(a)(8) requires that all
requirements applicable to major
stationary sources and major
modifications of VOCs shall apply to
NOX except where the Administrator
has granted a NOX waiver applying the
standards set forth under CAA section
182(f) and the waiver continues to
apply. In its submittal, Indiana certifies
that 326 IAC 2–3–1(y) and 326 IAC 2–
3–2(a) and (b) meet this requirement.
326 IAC 2–3–1(y) defines major
modification. As discussed above, 326
IAC 2–3–1(y)(1) is consistent with 40
CFR 51.165(a)(8) since it considers
increases in both VOC and NOX unless
a NOX waiver is in effect. 326 IAC 2–
3–1(y) considers, in serious and severe
ozone nonattainment areas, increases in
VOC or NOX unless a NOX waiver is in
effect and is consistent with 40 CFR
51.165(a)(8). 326 IAC 2–3–1(y) remains
consistent with the definition of major
modification at 40 CFR
51.165(a)(1)(v)(A) through (E) for
marginal and moderate ozone
nonattainment areas.
326 IAC 2–3–2(a) states that ozone
nonattainment NSR applies to new
major stationary sources or major
modifications in an area designated as
nonattainment for which the stationary
source or modification is major. As
previously discussed, 326 IAC 2–3–
1(z)(1), (2), and (5) and 326 IAC 2–3–
1(y) define major source and major
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modification, respectively, as they relate
to ozone nonattainment areas and
remain consistent with 40 CFR
51.165(a)(8).
326 IAC 2–3–2(b) applies to
modifications of VOC and NOX major
stationary sources in serious and severe
ozone nonattainment areas. 326 IAC 2–
3–2(b)(1) through (3) remain consistent
with CAA sections 182(c)(6) through (8)
and 182(d).
9. 40 CFR 51.165(a)(9)(ii)–(iv)—Offset
Ratios for VOC and NOX for Ozone
Nonattainment Areas
40 CFR 51.165(a)(9)(ii)(A)–(D)
requires the VOC offset ratio to be 1.1:1
in marginal ozone nonattainment areas,
1.15:1 in moderate ozone nonattainment
areas, 1.2:1 in serious ozone
nonattainment areas, and 1.3:1 in severe
ozone nonattainment areas. 326 IAC 2–
3–3(a)(5)(B) requires offset ratios for
both VOC and NOX that are consistent
with 40 CFR 51.165(a)(9)(ii)(A)–(D).
40 CFR 51.165(a)(9)(iv) requires, for
ozone nonattainment areas subject to
CAA Title I, Part D, Subpart 1 but not
Subpart 2, an offset ratio of at least 1:1.
All of the current ozone nonattainment
areas in Indiana were designated
pursuant to CAA Title I, Part D, Subpart
2, so this requirement does not apply to
Indiana at this time.
10. 40 CFR 51.165(a)(12)—Antibacksliding Provisions
40 CFR 51.165(a)(12) requires antiBacksliding requirements at 40 CFR
51.1105 to apply in any area designated
nonattainment for the 2008 ozone
NAAQS and designated nonattainment
for the 1997 ozone NAAQS on April 6,
2015. Indiana certified that there were
no areas designated as nonattainment
for the 1997 8-hour ozone NAAQS on
April 6, 2015.
40 CFR 81.315 provides the
attainment status designations for
Indiana. For the 1997 8-hour ozone
NAAQS, 40 CFR 81.315 codifies the fact
that all areas in Indiana attained the
1997 8-hour ozone NAAQS prior to
April 6, 2015. Table 10 includes
relevant information about the 1997 8hour ozone NAAQS, including the date
that areas previously designated as
nonattainment under the 1997 8-hour
ozone NAAQS were redesignated to
attainment. All other areas in Indiana
that are not listed in the table were
designated unclassifiable/attainment for
the 1997 8-hour ozone standard on June
15, 2004.28
TABLE 10—1997 8-HOUR OZONE NAAQS REDESIGNATION DATES AND Federal Register CITATIONS
Counties
Chicago-Gary-Lake County, IL-IN ............................
Cincinnati-Hamilton OH-KY-IN .................................
Evansville, IN ...........................................................
Fort Wayne, IN .........................................................
Greene Co., IN .........................................................
Indianapolis, IN ........................................................
Lake, Porter .............................................................
Dearborn (part) ........................................................
Vanderburgh, Warrick ..............................................
Allen .........................................................................
Greene .....................................................................
Boone, Hamilton, Hancock, Hendricks, Johnson,
Madison, Marion, Morgan, Shelby.
Jackson ....................................................................
LaPorte .....................................................................
Clark, Floyd ..............................................................
Delaware ..................................................................
Elkhart, St. Joseph ...................................................
Vigo ..........................................................................
Jackson Co., IN ........................................................
LaPorte Co., IN ........................................................
Louisville, KY-IN .......................................................
Muncie, IN ................................................................
South Bend-Elkhart, IN ............................................
Terre Haute, IN ........................................................
Since all areas in Indiana were
designated as attainment or
unclassifiable/attainment on April 6,
2015 for the 1997 8-hour ozone NAAQS,
the anti-backsliding requirements of 40
CFR 51.165(a)(12) do not apply for the
2008 8-hour ozone NAAQS.
11. Conclusion
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Redesignation
date
Designated areas
Indiana’s nonattainment NSR rules,
codified at 326 IAC 2–3, remain
consistent with Federal marginal and
moderate ozone nonattainment NSR
rules codified at 40 CFR 51.165.
Therefore, EPA is proposing to approve
Indiana’s certification that its
nonattainment NSR rules at 326 IAC 2–
3 meet the requirements of 40 CFR
51.165 and CAA sections 172(c)(5), 173,
110(a)(2), 182(a)(4), and 182(b)(5) for the
Indiana portion of the Chicago area
ozone nonattainment area. EPA’s final
approval of Indiana’s nonattainment
NSR certification will permanently stop
the sanctions and FIP clocks triggered
28 See
by EPA’s February 3, 2017 finding that
Indiana failed to submit a marginal
ozone nonattainment NSR plan.
16:30 Aug 27, 2018
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5/11/2010
5/11/2010
1/30/2006
2/12/2007
12/29/2005
10/19/2007
75
75
70
72
70
72
FR
FR
FR
FR
FR
FR
26113
26118
77026
1292
69085
59210
12/29/2005
7/19/2007
7/19/2007
1/3/2006
7/19/2007
2/6/2006
70
72
72
70
72
71
FR
FR
FR
FR
FR
FR
69085
39574
39571
69443
39577
541
submit a marginal ozone nonattainment
NSR plan.
III. What action is EPA proposing?
IV. Statutory and Executive Order
Reviews
EPA is proposing to approve revisions
to Indiana’s SIP pursuant to section 110
and part D of the CAA and EPA’s
regulations because Indiana’s February
28, 2017, nonattainment plan
submission and January 1, 2018,
supplement satisfy the emissions
inventory, RFP, RFP contingency
measures, transportation conformity,
VOC RACT, I/M, and nonattainment
NSR requirements of the CAA for the
Indiana portion of the Chicago area for
the 2008 ozone NAAQS. Final approval
of Indiana’s SIP as meeting the
nonattainment NSR requirements of the
CAA for the 2008 ozone NAAQS will
permanently stop the sanctions and FIP
clocks triggered by EPA’s February 3,
2017 finding that Indiana failed to
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,
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);
69 FR 23857.
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• 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 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).
In addition, the SIP is not approved
to apply on any Indian reservation land
or in any other area where EPA or an
Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, the rule does not have
tribal implications and will not impose
substantial direct costs on tribal
governments or preempt tribal law as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000).
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List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Ozone, Reporting and recordkeeping
requirements, Volatile organic
compounds.
Dated: August 16, 2018.
Cathy Stepp,
Regional Administrator, Region 5.
[FR Doc. 2018–18640 Filed 8–27–18; 8:45 am]
BILLING CODE 6560–50–P
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R03–OAR–2017–0633; FRL–9982–
79—Region 3]
Approval and Promulgation of Air
Quality Implementation Plans; West
Virginia; Revisions to Regulation for
Control of Ozone Season Nitrogen
Oxide Emissions
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
The Environmental Protection
Agency (EPA) is proposing to approve
two state implementation plan (SIP)
revisions submitted by the State of West
Virginia. The revisions pertain to a West
Virginia regulation that established the
nitrogen oxides (NOX) ozone season
trading program under the Clean Air
Interstate Rule (CAIR), which
implemented requirements for NOX
reductions necessary to reduce
interstate transport of pollution. The
EPA-administered trading programs
under CAIR were discontinued upon the
implementation of the Cross-State Air
Pollution Rule (CSAPR), which was
promulgated by EPA to replace CAIR.
CSAPR established federal
implementation plans (FIPs) for 28
states, including West Virginia, and
applied to electric generating units
(EGUs) as defined. The SIP submittals
are comprised of revisions to the West
Virginia regulation that implemented
the CAIR ozone season NOX trading
program and that had previously been
included in the West Virginia SIP. The
revised West Virginia regulation
removed the CAIR ozone season NOX
trading program provisions, which also
addressed certain large non-electric
generating units (non-EGUs),
established new requirements for these
large non-EGUs, included a state-wide
NOX emissions cap, and recodified
certain other provisions that address the
NOX emission reductions required for
cement kilns and internal combustion
engines. This action is being taken
under the Clean Air Act (CAA).
DATES: Written comments must be
received on or before September 27,
2018.
SUMMARY:
Submit your comments,
identified by Docket ID No. EPA–R03–
OAR–2017- 0633 at https://
www.regulations.gov, or via email to
spielberger.susan@epa.gov. For
comments submitted at Regulations.gov,
follow the online instructions for
submitting comments. Once submitted,
ADDRESSES:
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comments cannot be edited or removed
from Regulations.gov. For either manner
of submission, 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, please contact the person
identified in the ‘‘For Further
Information Contact’’ section. For 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:
Marilyn Powers, (215) 814–2308, or by
email at powers.marilyn@epa.gov.
SUPPLEMENTARY INFORMATION: On July
13, 2016, the State of West Virginia,
through the West Virginia Department
of Environmental Protection (WVDEP),
submitted a revised version of West
Virginia Regulation 45CSR40—Control
of Ozone Season Nitrogen Oxides
Emissions for inclusion in the West
Virginia SIP. The revised 45CSR40
made the following changes—(1)
removed the provisions that
implemented the CAIR ozone season
trading program, (2) added new
requirements to address the NOX
reduction obligations for non-EGUs in
the State that were trading under the
CAIR ozone season trading program but
are no longer part of a trading program,
and (3) recodified the requirements that
applied to cement kilns and internal
combustion engines. On October 13,
2017, WVDEP provided a supplemental
SIP submission comprised of a
demonstration showing that NOX
emissions from applicable non-EGUs do
not exceed the West Virginia NOX
budget under the NOX SIP Call.
I. Background
On October 27, 1998 (63 FR 57356),
EPA finalized the ‘‘Finding of
Significant Contribution and
Rulemaking for Certain States in the
Ozone Transport Assessment Group
Region for Purposes of Reducing
Regional Transport of Ozone’’—
commonly called the NOX SIP Call. The
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[Federal Register Volume 83, Number 167 (Tuesday, August 28, 2018)]
[Proposed Rules]
[Pages 43825-43836]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-18640]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R05-OAR-2017-0147; FRL-9982-90--Region 5]
Air Plan Approval; Indiana; Reasonable Further Progress Plan and
Other Plan Elements for the Chicago Nonattainment Area for the 2008
Ozone Standard
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is proposing to
approve a revision to the Indiana State Implementation Plan (SIP) to
meet the base year emissions inventory, reasonable further progress
(RFP), RFP contingency measure, nonattainment new source review
(nonattainment NSR), volatile organic compound (VOC) reasonably
available control technology (RACT), and motor vehicle inspection and
maintenance (I/M) requirements of the Clean Air Act (CAA) for the
Indiana portion of the Chicago-Naperville, Illinois-Indiana-Wisconsin
area (Chicago area) for the 2008 ozone national ambient air quality
standard (NAAQS or standard). EPA is also proposing to approve the 2017
transportation conformity motor vehicle emissions budgets (MVEBs) for
the Indiana portion of the Chicago area for the 2008 ozone NAAQS. EPA
is proposing to approve the state's submission as a SIP revision
pursuant to section 110 and part D of the CAA and EPA's regulations
because it satisfies the emission inventory, RFP, RFP contingency
measure, nonattainment NSR, VOC RACT, I/M, and transportation
conformity requirements for areas classified as moderate
[[Page 43826]]
nonattainment for the 2008 ozone NAAQS. Final approval of Indiana's SIP
as meeting the nonattainment NSR requirements of the CAA for the 2008
ozone NAAQS will permanently stop the sanctions and Federal
Implementation Plan (FIP) clocks triggered by EPA's February 3, 2017
finding that Indiana failed to submit a marginal ozone nonattainment
NSR plan.
DATES: Comments must be received on or before September 27, 2018.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R05-
OAR-2017-0147, at https://www.regulations.gov, or via email to
[email protected]. For comments submitted at Regulations.gov,
follow the online instructions for submitting comments. Once submitted,
comments cannot be edited or removed from Regulations.gov. For either
manner of submission, 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, please contact the person
identified in the FOR FURTHER INFORMATION CONTACT section. For 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: Kathleen D'Agostino, Environmental
Engineer, Attainment Planning and Maintenance Section, Air Programs
Branch (AR-18J), U.S. Environmental Protection Agency, Region 5, 77
West Jackson Boulevard, Chicago, Illinois 60604, (312) 886-1767,
[email protected].
SUPPLEMENTARY INFORMATION: Throughout this document, whenever ``we,''
``us,'' or ``our'' is used, we mean EPA. This supplementary information
section is arranged as follows:
I. What is the background for this action?
II. What is EPA's evaluation of Indiana's submittal?
III. What action is EPA proposing?
IV. Statutory and Executive Order Reviews
I. What is the background for this action?
A. Background on the 2008 Ozone Standard
On March 12, 2008, EPA promulgated a revised 8-hour ozone NAAQS of
0.075 parts per million (ppm).\1\ Promulgation of a revised NAAQS
triggers a requirement for EPA to designate all areas of the country as
nonattainment, attainment, or unclassifiable for the NAAQS. For the
ozone NAAQS, this also involves classifying any nonattainment areas at
the time of designation.\2\ Ozone nonattainment areas are classified
based on the severity of their ozone levels (as determined based on the
area's ``design value,'' which represents air quality in the area for
the most recent 3 years). The classifications for ozone nonattainment
areas are marginal, moderate, serious, severe, and extreme.\3\
---------------------------------------------------------------------------
\1\ 73 FR 16436 (March 27, 2008), codified at 40 CFR 50.15.
\2\ CAA sections 107(d)(1) and 181(a)(1).
\3\ CAA section 181(a)(1).
---------------------------------------------------------------------------
Areas that EPA designates nonattainment for the ozone NAAQS are
subject to the general nonattainment area planning requirements of CAA
section 172 and also to the ozone-specific planning requirements of CAA
section 182. Ozone nonattainment areas in the lower classification
levels have fewer and/or less stringent mandatory air quality planning
and control requirements than those in higher classifications. For
marginal areas, a state is required to submit a baseline emissions
inventory, adopt provisions into the SIP requiring emissions statements
from stationary sources, and implement a nonattainment NSR program for
the relevant ozone NAAQS.\4\ For moderate areas, a state needs to
comply with the marginal area requirements, plus additional moderate
area requirements, including the requirement to submit a modeled
demonstration that the area will attain the NAAQS as expeditiously as
practicable but no later than 6 years after designation, the
requirement to submit an RFP plan, the requirement to adopt and
implement certain emissions controls, such as RACT and I/M, and the
requirement for greater emissions offsets for new or modified major
stationary sources under the state's nonattainment NSR program.\5\
---------------------------------------------------------------------------
\4\ CAA section 182(a).
\5\ CAA section 182(b).
---------------------------------------------------------------------------
B. Background on the Chicago 2008 Ozone Nonattainment Area
On June 11, 2012,\6\ EPA designated the Chicago area as a marginal
nonattainment area for the 2008 ozone NAAQS. The Chicago area includes
Cook, DuPage, Kane, Lake, McHenry, and Will Counties and part of Grundy
and Kendall Counties in Illinois; Lake and Porter Counties in Indiana;
and part of Kenosha County in Wisconsin. On May 4, 2016,\7\ pursuant to
section 181(b)(2) of the CAA, EPA determined that the Chicago area
failed to attain the 2008 ozone NAAQS by the July 20, 2015, marginal
area attainment deadline and thus reclassified the area from marginal
to moderate nonattainment. In that action, EPA established January 1,
2017, as the due date for the state to submit all moderate area
nonattainment plan SIP requirements applicable to newly reclassified
areas.
---------------------------------------------------------------------------
\6\ 77 FR 34221, effective July 20, 2012.
\7\ 81 FR 26697.
---------------------------------------------------------------------------
In addition, effective March 6, 2017, EPA found that 15 states and
the District of Columbia failed to submit SIP revisions in a timely
manner to satisfy certain nonattainment plan requirements for the 2008
ozone NAAQS.\8\ This finding established certain deadlines for the
imposition of sanctions if a state does not submit a timely SIP
revision addressing the requirements for which EPA made the finding and
for EPA to promulgate a FIP to address any outstanding SIP
requirements. As part of that action, EPA made a finding that Indiana
failed to submit a SIP submission to meet the marginal nonattainment
NSR requirements for the Indiana portion of the Chicago area.
---------------------------------------------------------------------------
\8\ 82 FR 9158 (February 3, 2017).
---------------------------------------------------------------------------
II. What is EPA's evaluation of Indiana's submittal?
Indiana submitted a SIP revision request on February 28, 2017, and
submitted supplemental information on January 9, 2018, to address the
moderate area requirements for the Indiana portion of the Chicago area
for the 2008 ozone NAAQS. The submission contained a number of
nonattainment plan elements, including a revised 2011 base year
emissions inventory for VOC and oxides of nitrogen (NOX), a
15% RFP plan, a 3% RFP contingency measure plan, 2017 VOC and
NOX motor vehicle emissions budgets, a nonattainment NSR
certification, a VOC RACT certification, and an enhanced I/M
certification. The nonattainment NSR certification included in the SIP
submission addresses the deficiency that was the basis for the March 6,
2017,
[[Page 43827]]
finding; therefore, approval of this SIP revision would permanently
stop the sanctions and FIP clocks triggered by EPA's February 3, 2017
finding that Indiana failed to submit a marginal ozone nonattainment
NSR plan. The submission also included an attainment demonstration,
which will be addressed in a separate action.
A. Revised 2011 Base Year Emissions Inventory
CAA sections 172(c)(3) and 182(a)(1), 42 U.S.C. 7502(c)(3) and
7511a(a)(1), require states to develop and submit, as SIP revisions,
comprehensive, accurate, and complete emissions inventories for all
areas designated as nonattainment for the ozone NAAQS. An emissions
inventory for ozone is an estimation of actual emissions of VOC and
NOX from all sources located in the relevant designated
nonattainment area. For the 2008 ozone NAAQS, EPA has recommended that
states use 2011 as a base year for the emissions estimates.\9\ On April
7, 2017,\10\ EPA approved the 2011 base year emissions inventory
submitted by the Indiana Department of Environmental Management (IDEM)
on June 15, 2016, for the Indiana portion of the Chicago area. IDEM
included a revised 2011 base year emissions inventory in its February
27, 2017, submission. The revised 2011 base year emissions inventory
only modifies the emissions estimates for the on-road mobile sector,
with emissions estimates for point, area, and non-road mobile sectors
remaining unchanged from the inventory approved by EPA.
---------------------------------------------------------------------------
\9\ 78 FR 34178, 34190, (June 6, 2013).
\10\ 82 FR 16934.
---------------------------------------------------------------------------
In the original 2011 base year emissions inventory approved by EPA,
Indiana derived 2011 onroad mobile emissions by back-casting emissions
estimates generated by the MOVES2014 model for 2015 and 2020. The
revised onroad emissions estimates were generated by running the
MOVES2014 model for 2011. This is a more accurate method for estimating
2011 onroad emissions. Thus, EPA is proposing to approve the 2011 base
year emissions inventory the state submitted with the RFP plan as a
revision to the Indiana SIP.
Table 1--Revised 2011 Base Year Emissions Inventory in Tons per Summer Day
[tpsd]
--------------------------------------------------------------------------------------------------------------------------------------------------------
VOC NOX
Source sector -----------------------------------------------------------------------------------------------
Lake County Porter County Total Lake County Porter County Total
--------------------------------------------------------------------------------------------------------------------------------------------------------
EGU Point............................................... 0.44 0.19 0.63 24.62 5.53 30.15
Point................................................... 15.39 1.68 17.07 43.10 23.36 66.46
Area.................................................... 12.54 5.53 18.07 5.80 3.89 9.69
Non-road................................................ 7.55 6.64 14.19 8.07 4.62 12.69
On-road................................................. 6.92 2.66 9.58 17.85 6.85 24.70
-----------------------------------------------------------------------------------------------
Total............................................... 42.84 16.70 59.54 99.44 44.25 143.69
--------------------------------------------------------------------------------------------------------------------------------------------------------
B. 15% RFP Plan and 3% Contingency Plan
1. Background
The CAA requires that states with areas designated as nonattainment
for ozone achieve RFP toward attainment of the ozone NAAQS. CAA section
172(c)(2) contains a general requirement that nonattainment plans must
provide for emissions reductions that meet RFP. For areas classified
moderate and above, section 182(b)(1) imposes a more specific RFP
requirement that a state had to meet through a 15% reduction in VOC
emissions from the baseline anthropogenic emissions within 6 years
after November 15, 1990. The state must meet the 15% requirement by the
end of the 6-year period, regardless of when the nonattainment area
attains the NAAQS. As with other nonattainment plan requirements for
more recent iterations of the ozone NAAQS, EPA has promulgated
regulations and guidance to interpret the statutory requirements of the
CAA.
EPA's final rule to implement the 2008 ozone NAAQS (SIP
Requirements Rule),\11\ addressed, among other things, the RFP
requirements as they apply to areas designated nonattainment and
classified as moderate for the 2008 ozone NAAQS.\12\ EPA interprets the
15% VOC emission reduction requirement in CAA section 182(b)(1) such
that a state that has already met the 15% requirement for VOC for an
area under either the 1-hour ozone NAAQS or the 1997 8-hour ozone NAAQS
would not have to fulfill that requirement through reductions of VOC
again. Instead, EPA is interpreting CAA section 172(c)(2) to require
states with such areas to obtain 15% ozone precursor emission
reductions (VOC and/or NOX) over the first 6 years after the
baseline year for the 2008 ozone NAAQS. The state previously met the
15% VOC reduction requirement of CAA section 182(b)(1) for the Indiana
portion of the Chicago area under the 1-hour ozone NAAQS. Therefore,
the state may rely upon both VOC and NOX emissions
reductions to meet the RFP requirement for the 2008 ozone NAAQS.
---------------------------------------------------------------------------
\11\ 80 FR 12264. (March 6, 2015).
\12\ Ibid, at 12271 and 40 CFR 51.1110.
---------------------------------------------------------------------------
EPA's SIP Requirements Rule indicates the base year for the 2008
ozone NAAQS, for which areas were designated nonattainment effective
July 20, 2012, can be 2011 or a different year of the states choosing.
However, states selecting a pre-2011 alternate baseline year must
achieve 3% emission reductions each year after the initial 6-year
period has concluded up to the beginning of the attainment year. For a
multi-state area, states must agree on the same base year. Wisconsin,
Illinois, and Indiana have selected the EPA-recommended base year of
2011.\13\
---------------------------------------------------------------------------
\13\ On February 16, 2018, the D.C. Circuit Court issued a
decision in South Coast Air Quality Management District v. EPA, 882
F.3d 1138 (D.C. Cir. 2018), in which several parties challenged
different aspects of EPA's SIP Requirements Rule for the 2008 Ozone
NAAQS. In this decision, the Court upheld 2011 as a reasonable
baseline year for the 2008 ozone NAAQS but vacated the provision
allowing for an alternate year. Because Wisconsin, Illinois, and
Indiana have selected 2011 as the baseline year, the decision does
not impact Indiana's ROP plan.
---------------------------------------------------------------------------
States may not take credit for VOC or NOX reductions
occurring from sources outside the nonattainment area for purposes of
meeting the 15% ROP and 3% RFP requirements of CAA sections 172(c)(2),
182(b)(1) and 182(c)(2)(B). Indiana's 15% RFP represents emissions
reductions which occurred in Indiana's portion of the nonattainment
area from
[[Page 43828]]
2011 to 2017, thereby satisfying this requirement.
Except as specifically provided in section 182(b)(1)(D) of the CAA,
all state control measures approved into the SIP or Federal measures
that provide emissions reductions that occur after the baseline
emissions inventory year are creditable for purposes of the RFP
requirements, provided that the reductions meet the standard
requirements for creditability which include being enforceable,
quantifiable, permanent, and surplus in terms of not having previously
been counted toward RFP.
States must also include contingency measures in their
nonattainment plans. The contingency measures required for areas
classified as moderate and above under CAA sections 172(c)(9) and
182(c)(9) must provide for the implementation of specific measures if
the area fails to attain or to meet any applicable RFP milestone. The
state must submit these measures for approval by EPA into the SIP as
adopted measures that would take effect without further rulemaking
action by the state or the EPA upon a determination that an area failed
to attain or to meet the applicable milestone. Per EPA guidance for
purposes of the ozone NAAQS, contingency measures should represent one
year's worth of RFP progress, amounting to reductions of at least 3% of
the baseline emissions inventory for the nonattainment area.\14\ The
purpose of the contingency measures is to provide additional emission
reductions in the event of a failure to attain or meet any applicable
milestone, which would occur while the state is revising its SIP for
the area to rectify the failure to attain or to meet RFP
requirements.\15\
---------------------------------------------------------------------------
\14\ See the March 6, 2015 SIP Requirements Rule (80 FR 12264 at
12285) and April 16, 1992 General Preamble section III.A.3.c (57 FR
13498 at 13511).
\15\ 80 FR 12264 at 12285.
---------------------------------------------------------------------------
Regarding the contingency measures, EPA's prior guidance for
purposes of the ozone NAAQS specifies that some portion of the
contingency measures must include VOC reductions. This previous
limitation is no longer necessary in all areas. In particular, EPA has
concluded that states with nonattainment areas classified as moderate
and above that have already completed the initial 15% VOC reduction
required by CAA section 182(b)(1)(A)(i), can meet the contingency
measures requirement based entirely on NOX controls if that
is what the state's analyses have demonstrated would be most effective
in bringing the area into attainment. There is no minimum VOC
requirement. Also, EPA is continuing its long-standing policy that
allows states to use promulgated Federal measures as contingency
measures as long as they provide emission reductions in the relevant
years in excess of those needed for attainment or RFP.\16\
---------------------------------------------------------------------------
\16\ 80 FR 12264 at 12285.
---------------------------------------------------------------------------
2. Indiana's 15% RFP and 3% RFP Contingency Measures Plan
To demonstrate that the Indiana portion of the Chicago area has
achieved 15% RFP over the 6-year attainment planning period, Indiana is
using a 2011 base year inventory and a 2017 RFP inventory. To develop
the 2017 inventory, Indiana calculated on-road emissions using EPA's
MOVES2014 model and non-road emissions using EPA's National Mobile
Inventory Model (NMIM). The MOVES model for the on-road sector and NMIM
for the non-road sector incorporate a number of Federal emissions
control programs into its projections. These emissions reduction
measures are permanent and enforceable and are implemented in the
nonattainment area. The MOVES and NMIM models assumed increases in
vehicle or equipment population and usage while projecting decreases in
ozone precursor emissions from 2011 to 2017. The estimated emissions
reductions are therefore not due to reductions in source activity, but
to the implementation of control measures. Tables 2 and 3 list the
Federal permanent and enforceable control programs modeled by the MOVES
model for the on-road sector and NMIM for the non-road sector,
respectively.
Table 2--Federal On-Road Emission Control Programs Modeled by MOVES
----------------------------------------------------------------------------------------------------------------
On-road control program Pollutants Model year * Regulation
----------------------------------------------------------------------------------------------------------------
Passenger vehicles, SUVs, and light VOC & NOX.............. 2004-09+ (Tier 2) 2017+ 40 CFR parts 85 & 86.
duty trucks--emissions and fuel (Tier 3).
standards.
Light-duty trucks and medium duty VOC.................... 2004-10................ 40 CFR part 86.
passenger vehicle--evaporative
standards.
Heavy-duty highway compression engines VOC & NOX.............. 2007+.................. 40 CFR part 86.
Heavy-duty spark ignition engines..... VOC & NOX.............. 2005-08+............... 40 CFR part 86.
Motorcycles........................... VOC & NOX.............. 2006-10 (Tier 1 & 2)... 40 CFR part 86.
Mobile Source Air Toxics--fuel Organic Toxics & VOC... 2009-15 **............. 40 CFR parts 59, 80,
formulation, passenger vehicle 85, & 86.
emissions, and portable container
emissions.
Light duty vehicle corporate average Fuel efficiency (VOC & 2012-16 & 2017-25...... 40 CFR part 600.
fuel economy standards. NOX).
----------------------------------------------------------------------------------------------------------------
* The range in model years affected can reflect phasing of requirements based on engine size or initial years
for replacing earlier tier requirements.
** The range in model years reflects phased implementation of fuel, passenger vehicle, and portable container
emission requirements as well as the phasing by vehicle size and type.
Table 3--Federal Non-Road Emission Control Programs Modeled by NMIM
----------------------------------------------------------------------------------------------------------------
Nonroad control program * Pollutants Model year ** Regulation
----------------------------------------------------------------------------------------------------------------
Compression Ignition.................. VOC & NOX.............. 2000-2015+ (Tier 4).... 40 CFR parts 89 &
1039.
Large Spark Ignition.................. VOC & NOX.............. 2007+.................. 40 CFR part 1048.
Marine Spark Ignition................. VOC & NOX.............. 2010+.................. 40 CFR part 1045.
Recreational Vehicle.................. VOC & NOX.............. 2006-2012 (Tiers 1-3).. 40 CFR part 1051.
Small Spark Ignition Engine <19 Kw-- VOC & NOX.............. 2005-2012 (Tiers 2 & 3) 40 CFR parts 90 &
emission standards. 1054.
[[Page 43829]]
Small Spark Ignition Engine <19 Kw-- VOC.................... 2008-2016.............. 40 CFR parts 1045, 54,
evaporative standards. & 60.
----------------------------------------------------------------------------------------------------------------
* Compression ignition applies to diesel non-road compression engines including engines operated in
construction, agricultural, and mining equipment. Recreational vehicles include snowmobiles, off-road
motorcycles, and all-terrain vehicles. Small spark ignition engines include engines operated in lawn and hand-
held equipment.
** The range in model years affected can reflect phasing of requirements based on engine size or initial years
for replacing earlier tier requirements.
Indiana used the 2017 EPA-projected National Emissions Inventory
(NEI) to obtain estimated point and area source emissions. While EPA
projected point and area source emissions to decrease between 2011 and
2017, Indiana did not document the control programs and associated
reductions in emissions for these sectors or determine to what extent
any reduction may be attributed to reductions in source activity.
Therefore, Indiana took no credit for emissions reductions from these
source sectors in its RFP or RFP contingency measures calculations.
Table 4 shows Indiana's 2017 projected emissions inventory. Table 5
shows Indiana's 2017 RFP and RFP contingency emissions inventory, which
assumes no reduction in emissions between 2011 and 2017 from the point
and area source sectors.
Table 4--Projected 2017 Emissions Inventory
[tpsd]
--------------------------------------------------------------------------------------------------------------------------------------------------------
VOC NOX
Source sector -----------------------------------------------------------------------------------------------
Lake County Porter County Total Lake County Porter County Total
--------------------------------------------------------------------------------------------------------------------------------------------------------
EGU Point............................................... 0.09 0.07 0.16 4.07 1.36 5.43
Non-EGU Point........................................... 15.34 1.67 17.01 42.44 23.10 65.54
Area.................................................... 11.73 5.08 16.81 5.10 3.25 8.35
Non-road................................................ 5.03 4.44 9.47 5.59 3.48 9.07
On-road................................................. 4.33 1.63 5.96 10.15 4.35 14.50
-----------------------------------------------------------------------------------------------
Total............................................... 36.52 12.89 49.41 67.35 35.54 102.90
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table 5--2017 RFP AND RFP Contingency Measures Emissions Inventory
[tpsd]
--------------------------------------------------------------------------------------------------------------------------------------------------------
VOC NOX
Source sector -----------------------------------------------------------------------------------------------
Lake County Porter County Total Lake County Porter County Total
--------------------------------------------------------------------------------------------------------------------------------------------------------
EGU Point............................................... 0.44 0.19 0.63 24.62 5.53 30.15
Non-EGU Point........................................... 15.39 1.68 17.07 43.10 23.36 66.46
Area.................................................... 12.54 5.53 18.07 5.80 3.89 9.69
Non-road................................................ 5.03 4.44 9.47 5.59 3.48 9.07
On-road................................................. 4.33 1.63 5.96 10.15 4.35 14.50
-----------------------------------------------------------------------------------------------
Total............................................... 37.73 13.47 51.20 89.26 40.61 129.87
--------------------------------------------------------------------------------------------------------------------------------------------------------
Indiana submitted documentation showing that emission reductions in
the Indiana portion of the Chicago area met the 15% RFP and 3% RFP
contingency measures requirements entirely through Federal permanent
and enforceable control measures within the mobile source sectors.
Table 6 shows the calculations Indiana used to determine that the
mobile source emissions reductions meet the RFP and RFP contingency
measures requirements.
Table 6--2017 RFP and Contingency Target Level Calculations
[emissions in tpsd]
----------------------------------------------------------------------------------------------------------------
Description Formula VOC NOX
----------------------------------------------------------------------------------------------------------------
A. 2011 RFP Base Year Inventory.............................. ............... 59.54 143.69
B. RFP Reductions totaling 15%............................... ............... 9% 6%
C. RFP Emissions Reductions Required Between 2011 & 2017..... A * B 5.36 8.62
D. RFP Target Level for 2017................................. A-C 54.18 135.07
E. Contingency Percentage.................................... ............... 2% 1%
F. Contingency Emission Reduction Requirements............... A * E 1.2 1.44
G. RFP + Contingency Target Level............................ A-C-F 52.99 133.63
H. 2017 Projected Emissions (2017 RFP & Contingency ............... 51.20 129.87
Inventory)..................................................
I. Compare RFP & Contingency Target with 2017 Projected HX for ozone) to address pollution from on-road
transportation sources. The MVEBs are the portion of the total
allowable emissions that are allocated to highway and transit vehicle
use that, together with emissions from other sources in the area, will
meet an RFP milestone or provide for attainment or maintenance of the
NAAQS.\18\ The MVEB serves as a ceiling on emissions from an area's
planned transportation system.\19\
---------------------------------------------------------------------------
\17\ See the SIP requirements for the 2008 ozone standard in
EPA's March 6, 2015 implementation rule (80 FR 12264).
\18\ 40 CFR 93.101.
\19\ The MVEB concept is further explained in the preamble to
the November 24, 1993, Transportation Conformity Rule (58 FR 62188).
The preamble also describes how to establish the MVEB in the SIP and
how to revise the MVEB, if needed, subsequent to initially
establishing a MVEB in the SIP.
---------------------------------------------------------------------------
When reviewing control strategy or maintenance plan submissions,
EPA must affirmatively find that the MVEBs contained therein are
adequate for use in determining transportation conformity. Once EPA
affirmatively finds that the submitted MVEBs are adequate for
transportation purposes, the MVEBs must be used by state and Federal
agencies in determining whether proposed transportation projects
conform to the SIP as required by section 176(c) of the CAA.
EPA's substantive criteria for determining adequacy of a MVEB are
set out in 40 CFR 93.118(e)(4). The process
[[Page 43831]]
for determining adequacy consists of three basic steps: Public
notification of a SIP submission; provision for a public comment
period; and EPA's adequacy determination. This process for determining
the adequacy of submitted MVEBs for transportation conformity purposes
was initially outlined in EPA's May 14, 1999 guidance, ``Conformity
Guidance on Implementation of March 2, 1999, Conformity Court
Decision.'' EPA adopted regulations to codify the adequacy process in
the Transportation Conformity Rule Amendments for the ``New 8-Hour
Ozone and PM2.5 National Ambient Air Quality Standards and
Miscellaneous Revisions for Existing Areas; Transportation Conformity
Rule Amendments--Response to Court Decision and Additional Rule
Change,'' on July 1, 2004.\20\ Additional information on the adequacy
process for transportation conformity purposes is available in a June
30, 2003, proposed rule titled, ``Transportation Conformity Rule
Amendments: Response to Court Decision and Additional Rule Changes.''
\21\
---------------------------------------------------------------------------
\20\ 69 FR 40004.
\21\ 68 FR 38974, 38984.
---------------------------------------------------------------------------
Indiana's RFP and contingency measure plan includes VOC and
NOX MVEBs for the Indiana portion of the Chicago area for
2017. EPA reviewed the VOC and NOX MVEBs through the
adequacy process. Indiana's February 28, 2017, RFP and contingency
measure SIP submission (as supplemented on January 9, 2018), including
the VOC and NOX MVEBs for the Indiana portion of the Chicago
area, was available for public comment on EPA's adequacy website on
February 2, 2018, found at: https://www.epa.gov/otaq/stateresources/transconf/currsips.htm. The EPA public comment period on adequacy of
the 2017 MVEBs for the Indiana portion of the Chicago area closed on
March 5, 2018. No comments on the submittal were received during the
adequacy comment period. The submitted RFP and contingency measure
plan, which included the MVEBs, was endorsed by the Governor's designee
and was subject to a state public hearing. The MVEBs were developed as
part of an interagency consultation process which includes Federal,
state, and local agencies. The MVEBs were clearly identified and
precisely quantified. These MVEBs, when considered together with all
other emissions sources, are consistent with the 15% RFP and 3% RFP
contingency measures requirements of the 2008 8-hour ozone standard.
Table 7--2017 VOC and NOX MVEBs for the Indiana Portion of the Chicago Area
[tpsd]
--------------------------------------------------------------------------------------------------------------------------------------------------------
Allocation of surplus
2017 On-road emissions RFP + Contingency plan reductions to on-road 2017 MVEBs
surplus reductions mobile sector
--------------------------------------------------------------------------------------------------------------------------------------------------------
VOC................................................. 5.96 1.79 0.89 6.85
NOX................................................. 14.50 3.65 2.18 16.68
--------------------------------------------------------------------------------------------------------------------------------------------------------
As shown in Table 7, the 2017 MVEBs exceed the estimated 2017 on-
road sector emissions. In an effort to accommodate future variations in
travel demand models and vehicle miles traveled forecast, Indiana
allocated a portion of the surplus RFP and contingency plan reductions
to the mobile sector. Indiana has demonstrated that the Indiana portion
of the Chicago area can meet the 15% RFP and 3% RFP contingency measure
requirements of the 2008 ozone NAAQS with mobile source emissions of
6.85 tpsd of VOC and 16.68 tpsd of NOX in 2017, because
despite partial allocation of the RFP and RFP contingency measures plan
surplus reductions, emissions will remain under 2017 RFP plus
contingency measure target levels. EPA has found adequate and is thus
proposing to approve the 2017 VOC and NOX MVEBs for use to
determine transportation conformity in the Indiana portion of the
Chicago area under the 2008 ozone NAAQS because EPA has determined that
the area can meet the 15% RFP and 3% RFP contingency measure
requirements of the 2008 ozone NAAQS with mobile source emissions at
the levels of the MVEBs.
D. VOC RACT Certification
Sections 172(c)(1) and 182(b)(2) of the CAA require states to
implement RACT in ozone nonattainment areas classified as moderate (and
higher). Specifically, these areas are required to implement RACT for
all major VOC and NOX emissions sources and for all sources
covered by a Control Techniques Guideline (CTG). A CTG is a document
issued by EPA which establishes a ``presumptive norm'' for RACT for a
specific VOC source category. States must submit rules, or negative
declarations when no such sources exist for CTG source categories.
EPA's SIP Requirements Rule for the 2008 ozone NAAQS indicates that
states may meet RACT through the establishment of new or more stringent
requirements that meet RACT control levels, through a certification
that previously adopted RACT controls in their SIPs approved by EPA for
a prior ozone NAAQS also represent adequate RACT control levels for
attainment of the 2008 ozone NAAQS, or with a combination of these two
approaches. In addition, a state must submit a negative declaration in
instances where there are no CTG sources.
In its February 28, 2017 submission, Indiana certified that the
existing VOC rules contained in 326 Indiana Administrative Code (IAC) 8
satisfy the VOC RACT requirements of Section 182(b)(2) of the CAA and
have been approved into the SIP by EPA. Indiana also certified that the
negative declaration approved into the SIP by EPA for the fiberglass
boat manufacturing materials CTG is still current.\22\ Table 8 lists
these state regulations and identifies the associated SIP approvals by
EPA.
---------------------------------------------------------------------------
\22\ The NEI, the Harris Manufacturing Directory and the Manta
small business directory were reviewed to spot check the validity of
the previously approved negative declaration for this category. No
fiberglass boat manufacturing facilities subject to the CTG were
identified.
[[Page 43832]]
Table 8--VOC RACT Regulations Approved into the Indiana SIP
------------------------------------------------------------------------
Applicable Indiana EPA approval into
CTGs and ACTs \1\ regulation the SIP
------------------------------------------------------------------------
EPA 453/R-08-004 2008/09-- Negative 75 FR 8246 (02/24/
Control Techniques Guidelines Declaration 2010).
for Fiberglass Boat Letter--06/05/
Manufacturing Materials. 2009.
EPA 453/R-08-006, 2008/09-- 326 IAC 8-2-2--
Control Techniques Guidelines Automobile and
for Automobile and Light-Duty Light Duty Truck
Truck Assembly Coatings and EPA Coating
453/R-08-002, 2008/09--Protocol Operations.
for Determining the Daily
Volatile Organic Compound
Emission Rate of Automobile and
Light-Duty Truck Primer-
Surfacer and Topcoat Operations.
EPA 453/R-07-003, 2007/09-- 326 IAC 8-2-5--
Control Techniques Guidelines Paper Coating
for Paper, Film, and Foil Operations.
Coatings.
EPA 453/R-07-005, 2007/09-- 326 IAC 8-2-6--
Control Techniques Guidelines Metal Furniture
for Metal Furniture Coatings. Coating
Operations.
EPA 453/R-07-004, 2007/09-- 326 IAC 8-2-7--
Control Techniques Guidelines Large Appliance
for Large Appliance Coatings. Coating
Operations.
EPA 453/R-08-003, 2008/09-- 326 IAC 8-2-9-- 75 FR 8246 (02/24/
Control Techniques Guidelines Miscellaneous 2010) Revision:
for Miscellaneous Metal and Metal and Plastic 76 FR 63549 (10/
Plastic Parts Coatings. Parts Coating 13/2011).
Operations.
EPA-453/R-06-004 2006/09-- 326 IAC 8-2-10-- 75 FR 8246 (02/24/
Control Techniques Guidelines Flat Wood Panels; 2010).
for Flat Wood Paneling Coatings. Manufacturing
Operations.
EPA-453/R-06-003 2006/09-- 326 IAC 8-5-5-- 63 FR 35141 (06/29/
Control Techniques Guidelines Graphic Arts and 1998) and 75 FR
for Flexible Package Printing. Graphic Arts 8246 (02/24/
Operations. 2010).
Non-CTG......................... IAC 326 8-7-- 60 FR 34856 (07/05/
Specific VOC 1995).
Reduction
Requirements for
Lake, Porter,
Clark, and Floyd
Counties.
EPA-453/R-06-002 2006/09-- 326 IAC 8-16-- 75 FR 8246 (02/24/
Control Techniques Guidelines Offset 2010).
for Offset Lithographic Lithographic
Printing and Letterpress Printing and
Printing. Letterpress
Printing.
EPA-453/R-06-001, 2006/09-- 326 IAC 8-17--
Control Techniques Guidelines Industrial
for Industrial Cleaning Solvent Cleaning
Solvents. Operations.
EPA-450/3-84-015 1984/12-- 326 IAC 8-18--
Control of Volatile Organic Synthetic Organic
Compound Emissions from Air Chemical
Oxidation Processes in Manufacturing
Synthetic Organic Chemical Industry Air
Manufacturing Industry and EPA- Oxidation,
450/4-91-031 1993/08--Control Distillation, and
of Volatile Organic Compound Reactor
Emissions from Reactor Processes.
Processes and Distillation
Operations in Synthetic Organic
Chemical Manufacturing Industry.
EPA-453/R-93-020, 1994/02-- 326 IAC 8-19--
Control of Volatile Organic Control of
Compound Emissions from Batch Volatile Organic
Processes ACT (Note--also Compound
released as EPA-453/R-93-017). Emissions from
Process Vents in
Batch Operations.
EPA-453/D-93-056, 1992/09-- 326 IAC 8-20--
Control of Volatile Organic Industrial
Compound Emissions from Wastewater.
Industrial Wastewater CTG
(draft).
Note--CTG not finalized but
issued as ACT in 1994..
(No Report ID) 1994/04
Industrial Wastewater
Alternative Control Technology..
Note--ACT consists of cover memo
with option tables + CTG
(draft) EPA-453/D-93-056..
59 FR-29216, 6/06/94--1994/06 326 IAC 8-21--
Aerospace MACT and EPA-453/R-97- Aerospace
004, 1997/12 Aerospace (CTG & Manufacturing and
MACT). Rework
Operations.
EPA 453/R-08-005, 2008/09-- 326 IAC 8-22--
Control Techniques Guidelines Miscellaneous
for Miscellaneous Industrial Industrial
Adhesives. Adhesives.
------------------------------------------------------------------------
\1\ ACTs describe available control technologies and their respective
cost effectiveness but do not establish presumptive RACT.
EPA has reviewed Indiana's certification that it has adopted VOC
control regulations for stationary sources that constitute RACT, and
determined that the set of regulations cited by the state and negative
declaration for fiberglass boat manufacturing constitute RACT for
purposes of the 2008 ozone NAAQS in this nonattainment area. Therefore,
EPA is proposing to approve the state's submission as meeting the VOC
RACT requirements for the Indiana portion of the Chicago area for the
2008 ozone NAAQS.
E. Motor Vehicle I/M Program Certification
The requirement to adopt a motor vehicle I/M program for moderate
ozone nonattainment areas is described in CAA section 182(b)(4), and
the regulations for basic and enhanced I/M programs are found at 40 CFR
part 51, subpart S. Under these cumulative requirements, states with
areas classified as moderate nonattainment for ozone with 1990 Census-
defined urbanized populations of 200,000 or more are required to adopt
basic I/M programs, while serious and higher classified ozone
nonattainment areas outside of the northeast ozone transport region
with 1980 Census-defined urbanized populations of 200,000 or more are
required to adopt enhanced I/M programs. The Chicago area meets the
criteria for mandatory I/M under the 2008 ozone NAAQS.
The Indiana portion of the Chicago area was required to adopt an
enhanced I/M program under the 1-hour ozone NAAQS. EPA approved
Indiana's enhanced I/M program on March 19, 1996 (61 FR 11142).
Indiana's I/M program is authorized by state statute
[[Page 43833]]
Indiana Code (IC) 13-17-5, paid through the general funds, and
implemented through rules promulgated by the Indiana Environmental
Rules Board at 326 IAC 13. These requirements remain in place in
Indiana's ozone SIP. In its February 28, 2017, submission, Indiana
certified that the existing enhanced I/M program continues to satisfy
the I/M requirements of the CAA for the Indiana portion of the Chicago
area. Therefore, EPA is proposing to find that Indiana has met the I/M
requirement for its portion of the Chicago area for the 2008 ozone
NAAQS.
F. Nonattainment New Source Review
1. Background
CAA sections 110(a)(2) and 172(c)(5) require permits for the
construction of new or modified major stationary sources anywhere in a
nonattainment area in accordance with CAA section 173. CAA section 182
contains additional requirements applicable to ozone nonattainment
areas. Nonattainment NSR requirements are codified at 40 CFR 51.165.
On March 6, 2017, EPA found that Indiana failed to submit marginal
ozone nonattainment NSR rules for the Indiana portions of the Chicago
area and Cincinnati \23\ 2008 ozone nonattainment areas.\24\ On
February 28, 2017, Indiana submitted its nonattainment NSR
certification to address nonattainment NSR requirements for marginal
and moderate ozone nonattainment areas.\25\
---------------------------------------------------------------------------
\23\ The Cincinnati, Ohio-Kentucky-Indiana 8-hour ozone
nonattainment area has since been redesignated to attainment
effective April 7, 2017. See 82 FR 16940.
\24\ See 82 FR 9158.
\25\ The Chicago-Naperville 2008 8-hour ozone nonattainment area
was reclassified to moderate nonattainment effective June 3, 2017.
See 81 FR 26697.
---------------------------------------------------------------------------
Indiana has certified that specific sections of its nonattainment
NSR rules at 326 IAC 2-3 continue to meet the nonattainment NSR program
requirements for ozone nonattainment areas under the 2008 ozone NAAQS.
Table 9 provides the sections of Indiana's nonattainment NSR rule
corresponding to the relevant requirements at 40 CFR 51.165. 326 IAC 2-
3 was originally approved into the SIP effective December 6, 1994,\26\
with revisions subsequently approved into the SIP effective September
6, 2011.\27\ Each requirement identified in Indiana's certification has
been unchanged since EPA last approved it.
---------------------------------------------------------------------------
\26\ See 59 FR 51108. In its submittal, Indiana cites 94 FR
24838 as the initial approval for each requirement. The Federal
Register Document Number of the initial approval is 94-24838 and
corresponds to the proposed Approval and Promulgation of a New
Source Review Implementation Plan; Indiana. Federal Register
Document Number 94-24837 is the direct final Approval and
Promulgation of a New Source Review Implementation Plan; Indiana.
The direct final rule can be found at 59 FR 51108. Throughout
today's proposed rule, the direct final approval of Indiana's NSR
program will be cited as 59 FR 51108.
\27\ See 76 FR 40242.
Table 9--Nonattainment NSR Rules Indiana Certified as Meeting Federal Rules
----------------------------------------------------------------------------------------------------------------
Federal rule Indiana rule
----------------------------------------------------------------------------------------------------------------
40 CFR 51.165(a)(1)(iv)(A)(1)(i)-(iii). 326 IAC 2-3-1(z)(1) and (2).
40 CFR 51.165(a)(1)(iv)(A)(2).......... 326 IAC 2-3-1(z)(1) and (2).
40 CFR 51.165(a)(1)(iv)(A)(3).......... 326 IAC 2-3-1(z)(5).
40 CFR 51.165(a)(1)(v)(E).............. 326 IAC 2-3-1(y)(1).
40 CFR 51.165(a)(1)(x)(A)-(C).......... 326 IAC 2-3-1(pp).
40 CFR 51.165(a)(3)(ii)(C)(1)-(2)...... 326 IAC 2-3-3(b)(5).
40 CFR 51.165(a)(8).................... 326 IAC 2-3-1(y); 326 IAC 2-3-2(a) and (b).
40 CFR 51.165(a)(9)(ii)-(iv)........... 326 IAC 2-3-3(a)(5)(B).
----------------------------------------------------------------------------------------------------------------
For the following reasons, we are proposing to approve Indiana's
certification that 326 IAC 2-3 is consistent with 40 CFR 51.165 and
meets the requirements of CAA sections 172(c)(5), 173, 110(a)(2),
182(a)(4), and 182(b)(5) under the 2008 ozone standard for the Indiana
portion of the Chicago area ozone nonattainment area. Approval of
Indiana's nonattainment NSR certification would address the deficiency
that was the basis for the March 6, 2017 finding. Therefore, final
approval of this SIP revision will permanently stop the sanctions and
FIP clocks triggered by EPA's February 3, 2017 finding that Indiana
failed to submit a marginal ozone nonattainment NSR plan.
2. Extreme Ozone Nonattainment Area and Ozone Transport Region
Nonattainment NSR Requirements
In its February 28, 2017 submission, Indiana states that its
nonattainment NSR rules do not include extreme ozone nonattainment
requirements because Indiana has never had an extreme ozone
nonattainment area. We concur with the statement that Indiana has never
had an extreme ozone nonattainment area. Further, the finding of
failure to submit applies to marginal ozone nonattainment NSR
requirements, not extreme. Finally, the Chicago area ozone
nonattainment area was reclassified to a moderate ozone nonattainment
area which requires moderate, not extreme, ozone nonattainment NSR
requirements. For these reasons, Indiana's nonattainment NSR program
does not require extreme ozone nonattainment requirements at this time.
The following extreme ozone nonattainment NSR requirements are not
included as part of Indiana's nonattainment NSR rules: 40 CFR
51.165(a)(1)(iv)(A)(1)(iv), 40 CFR 51.165(a)(1)(iv)(A)(2)(vi), 40 CFR
51.165(a)(1)(v)(F), 40 CFR 51.165(a)(1)(x)(E), and 40 CFR
51.165(a)(9)(ii)(E).
Indiana's submission does not address ozone transport region
requirements. However, no portion of Indiana is currently part of an
ozone transport region; therefore, ozone transport region nonattainment
NSR requirements do not apply in Indiana. The following ozone transport
region nonattainment NSR requirements are not included as part of
Indiana's nonattainment NSR rules: 40 CFR 51.165(a)(1)(iv)(A)(1)(ii),
40 CFR 51.165(a)(1)(iv)(A)(2)(ii), 40 CFR 51.165(a)(1)(iv)(A)(2)(ii),
40 CFR 51.165(a)(1)(v)(E), 40 CFR 51.165(a)(1)(x)(C), 40 CFR
51.165(a)(8), and 40 CFR 51.165(a)(9)(iii).
Extreme ozone nonattainment area and ozone transport region
nonattainment NSR requirements will not be addressed further in this
analysis of Indiana's ozone nonattainment NSR program certification
because they do not apply to Indiana at this time. If, in the future,
Indiana has an extreme ozone nonattainment area or becomes part of an
ozone transport region, then
[[Page 43834]]
Indiana's SIP would need to be revised to establish the appropriate
nonattainment NSR requirements.
3. 40 CFR 51.165(a)(1)(iv)(A)(1)(i)-(iv) and (2)--Major Source
Thresholds for Ozone
40 CFR 51.165(a)(1)(iv)(A)(1)(i)-(iv) and (2) defines the major
source thresholds for the ozone precursors VOC and NOX. The
major source threshold for both VOC and NOX vary depending
on the classification of the ozone nonattainment area. For marginal and
moderate ozone nonattainment areas, a major stationary source of ozone
is a source that emits, or has the potential to emit, 100 tons per year
or more of VOC or NOX. Different emissions thresholds apply
for serious, severe, and extreme ozone nonattainment areas and areas in
an ozone transport region.
326 IAC 2-3-1(z)(1) generally defines a major stationary source as
a stationary source that emits, or has the potential to emit, 100 tons
per year or more of any regulated NSR pollutant, with an exception for
ozone provided in 326 IAC 2-3-1(z)(2). 326 IAC 2-3-1(z)(2) defines a
major stationary source for ozone nonattainment areas, specifying that
the major source threshold is 100 tons per year or more of VOC or
NOX in marginal and moderate ozone nonattainment areas. 326
IAC 2-3-1(z)(1) and (2) remain consistent with 40 CFR
51.165(a)(1)(iv)(A)(1)(i)-(iv) and (2) for marginal and moderate ozone
nonattainment areas.
4. 40 CFR 51.165(a)(1)(iv)(A)(3)--Change Constitutes Major Source by
Itself
40 CFR 51.165(a)(1)(iv)(A)(3) requires any physical change that
would constitute a major stationary source by itself to be treated as a
major stationary source if the stationary source does not qualify as a
major stationary source. 326 IAC 2-3-1(z)(5) requires the same and
remains consistent with 40 CFR 51.165(a)(1)(iv)(A)(3).
5. 40 CFR 51.165(a)(1)(v)(E)--Significant Net Emissions Increase of
NOX is Significant for Ozone
40 CFR 51.165(a)(1)(v)(E) requires significant net emissions
increases of NOX to be considered significant for ozone. For
major modifications, 326 IAC 2-3-1(y)(1) requires significant net
emissions increases of NOX to be considered significant for
ozone in ozone nonattainment areas. 326 IAC 2-3-1(y)(1) exempts
NOX when the Administrator has granted a NOX
waiver pursuant to CAA section 182(f) and 40 CFR 51.165(a)(8). As a
result, 326 IAC 2-3-1(y)(1) remains consistent with 40 CFR
51.165(a)(1)(v)(E).
6. 40 CFR 51.165(a)(1)(x)(A)-(C)--Significant Emission Rates for VOC
and NOX as Ozone Precursors
40 CFR 51.165(a)(1)(x)(A) defines the significant emission rate for
ozone as 40 tons per year of VOC or NOX. 326 IAC 2-3-1(pp)
defines the significant emission rate for ozone in marginal and
moderate nonattainment areas as 40 tons per year of VOC or
NOX (unless a NOX waiver is in effect). 326 IAC
2-3-1(pp) remains consistent with 40 CFR 51.165(a)(1)(x)(A) for
marginal and moderate ozone nonattainment areas.
40 CFR 51.165(a)(1)(x)(B) and (C) define the significant emission
rate for ozone in serious or severe nonattainment areas as 25 tons per
year of VOC or NOX. For the purpose of implementing
nonattainment NSR in marginal and moderate ozone nonattainment areas,
serious and severe ozone significant emission rates are not required.
7. 40 CFR 51.165(a)(3)(ii)(C)(1)-(2)--Provisions for Emissions
Reduction Credits
40 CFR 51.165(a)(3)(ii)(C)(1) and (2) are the requirements that
make emission reductions achieved by shutting down an existing emission
unit or curtailing production or operating hours creditable. Such
reductions must be surplus, permanent, quantifiable, and federally
enforceable. Shutdowns or curtailments must have occurred after the
last day of the base year for the SIP planning process. Reviewing
authorities may choose to consider a prior shutdown or curtailment to
have occurred after the last day of the base year if the projected
emissions inventory used to develop the attainment demonstration
explicitly includes emissions from the previously shutdown or curtailed
emissions units, but in no event may credit be granted for shutdowns
that occurred prior to August 7, 1977. Shutdown or curtailment
reductions occurring before the last day of the base year for the SIP
planning process may also be generally credited if the shutdown or
curtailment occurred on or after the date the construction permit
application is filed or if the applicant can establish that the
proposed new emissions unit is a replacement for the shutdown or
curtailed emission unit and the emission reductions that result are
surplus, permanent, quantifiable, and federally enforceable. 326 IAC 2-
3-3(b)(5) remains consistent with 40 CFR 51.165(a)(3)(ii)(C)(1)(i) and
40 CFR 51.165(a)(3)(ii)(C)(2)(ii).
326 IAC 2-3-3(b)(5)(A) credits emission reductions from emission
unit shutdowns and curtailments if they occurred on or after the date
of the most recent emissions inventory or attainment demonstration.
Prior shutdown or curtailment emission reductions may be considered to
have occurred after the date of the most recent emissions inventory if
the inventory explicitly includes the emissions from the previously
shutdown or curtailed emissions units. 326 IAC 2-3-3(b)(5)(A) remains
consistent with 40 CFR 51.165(a)(3)(ii)(C)(1)(ii).
326 IAC 2-3-3(b)(5)(B) allows reductions to be credited absent an
approved attainment demonstration if the shutdown or curtailment
occurred on or after the date the new source permit application is
filed or if the applicant can establish that the proposed new source is
a replacement for the shutdown or curtailed emissions unit, with the
exception of shutdowns occurring prior to August 7, 1977. 326 IAC 2-3-
3(b)(5)(B) remains consistent with 40 CFR 51.165(a)(3)(ii)(C)(2)(ii).
8. 40 CFR 51.165(a)(8)--Requirements for VOC Apply to NOX as
Ozone Precursors
40 CFR 51.165(a)(8) requires that all requirements applicable to
major stationary sources and major modifications of VOCs shall apply to
NOX except where the Administrator has granted a
NOX waiver applying the standards set forth under CAA
section 182(f) and the waiver continues to apply. In its submittal,
Indiana certifies that 326 IAC 2-3-1(y) and 326 IAC 2-3-2(a) and (b)
meet this requirement.
326 IAC 2-3-1(y) defines major modification. As discussed above,
326 IAC 2-3-1(y)(1) is consistent with 40 CFR 51.165(a)(8) since it
considers increases in both VOC and NOX unless a
NOX waiver is in effect. 326 IAC 2-3-1(y) considers, in
serious and severe ozone nonattainment areas, increases in VOC or
NOX unless a NOX waiver is in effect and is
consistent with 40 CFR 51.165(a)(8). 326 IAC 2-3-1(y) remains
consistent with the definition of major modification at 40 CFR
51.165(a)(1)(v)(A) through (E) for marginal and moderate ozone
nonattainment areas.
326 IAC 2-3-2(a) states that ozone nonattainment NSR applies to new
major stationary sources or major modifications in an area designated
as nonattainment for which the stationary source or modification is
major. As previously discussed, 326 IAC 2-3-1(z)(1), (2), and (5) and
326 IAC 2-3-1(y) define major source and major
[[Page 43835]]
modification, respectively, as they relate to ozone nonattainment areas
and remain consistent with 40 CFR 51.165(a)(8).
326 IAC 2-3-2(b) applies to modifications of VOC and NOX
major stationary sources in serious and severe ozone nonattainment
areas. 326 IAC 2-3-2(b)(1) through (3) remain consistent with CAA
sections 182(c)(6) through (8) and 182(d).
9. 40 CFR 51.165(a)(9)(ii)-(iv)--Offset Ratios for VOC and
NOX for Ozone Nonattainment Areas
40 CFR 51.165(a)(9)(ii)(A)-(D) requires the VOC offset ratio to be
1.1:1 in marginal ozone nonattainment areas, 1.15:1 in moderate ozone
nonattainment areas, 1.2:1 in serious ozone nonattainment areas, and
1.3:1 in severe ozone nonattainment areas. 326 IAC 2-3-3(a)(5)(B)
requires offset ratios for both VOC and NOX that are
consistent with 40 CFR 51.165(a)(9)(ii)(A)-(D).
40 CFR 51.165(a)(9)(iv) requires, for ozone nonattainment areas
subject to CAA Title I, Part D, Subpart 1 but not Subpart 2, an offset
ratio of at least 1:1. All of the current ozone nonattainment areas in
Indiana were designated pursuant to CAA Title I, Part D, Subpart 2, so
this requirement does not apply to Indiana at this time.
10. 40 CFR 51.165(a)(12)--Anti-backsliding Provisions
40 CFR 51.165(a)(12) requires anti-Backsliding requirements at 40
CFR 51.1105 to apply in any area designated nonattainment for the 2008
ozone NAAQS and designated nonattainment for the 1997 ozone NAAQS on
April 6, 2015. Indiana certified that there were no areas designated as
nonattainment for the 1997 8-hour ozone NAAQS on April 6, 2015.
40 CFR 81.315 provides the attainment status designations for
Indiana. For the 1997 8-hour ozone NAAQS, 40 CFR 81.315 codifies the
fact that all areas in Indiana attained the 1997 8-hour ozone NAAQS
prior to April 6, 2015. Table 10 includes relevant information about
the 1997 8-hour ozone NAAQS, including the date that areas previously
designated as nonattainment under the 1997 8-hour ozone NAAQS were
redesignated to attainment. All other areas in Indiana that are not
listed in the table were designated unclassifiable/attainment for the
1997 8-hour ozone standard on June 15, 2004.\28\
---------------------------------------------------------------------------
\28\ See 69 FR 23857.
Table 10--1997 8-Hour Ozone NAAQS Redesignation Dates and Federal Register Citations
----------------------------------------------------------------------------------------------------------------
Redesignation
Designated areas Counties date Federal Register citation
----------------------------------------------------------------------------------------------------------------
Chicago-Gary-Lake County, IL-IN...... Lake, Porter............ 5/11/2010 75 FR 26113
Cincinnati-Hamilton OH-KY-IN......... Dearborn (part)......... 5/11/2010 75 FR 26118
Evansville, IN....................... Vanderburgh, Warrick.... 1/30/2006 70 FR 77026
Fort Wayne, IN....................... Allen................... 2/12/2007 72 FR 1292
Greene Co., IN....................... Greene.................. 12/29/2005 70 FR 69085
Indianapolis, IN..................... Boone, Hamilton, 10/19/2007 72 FR 59210
Hancock, Hendricks,
Johnson, Madison,
Marion, Morgan, Shelby.
Jackson Co., IN...................... Jackson................. 12/29/2005 70 FR 69085
LaPorte Co., IN...................... LaPorte................. 7/19/2007 72 FR 39574
Louisville, KY-IN.................... Clark, Floyd............ 7/19/2007 72 FR 39571
Muncie, IN........................... Delaware................ 1/3/2006 70 FR 69443
South Bend-Elkhart, IN............... Elkhart, St. Joseph..... 7/19/2007 72 FR 39577
Terre Haute, IN...................... Vigo.................... 2/6/2006 71 FR 541
----------------------------------------------------------------------------------------------------------------
Since all areas in Indiana were designated as attainment or
unclassifiable/attainment on April 6, 2015 for the 1997 8-hour ozone
NAAQS, the anti-backsliding requirements of 40 CFR 51.165(a)(12) do not
apply for the 2008 8-hour ozone NAAQS.
11. Conclusion
Indiana's nonattainment NSR rules, codified at 326 IAC 2-3, remain
consistent with Federal marginal and moderate ozone nonattainment NSR
rules codified at 40 CFR 51.165. Therefore, EPA is proposing to approve
Indiana's certification that its nonattainment NSR rules at 326 IAC 2-3
meet the requirements of 40 CFR 51.165 and CAA sections 172(c)(5), 173,
110(a)(2), 182(a)(4), and 182(b)(5) for the Indiana portion of the
Chicago area ozone nonattainment area. EPA's final approval of
Indiana's nonattainment NSR certification will permanently stop the
sanctions and FIP clocks triggered by EPA's February 3, 2017 finding
that Indiana failed to submit a marginal ozone nonattainment NSR plan.
III. What action is EPA proposing?
EPA is proposing to approve revisions to Indiana's SIP pursuant to
section 110 and part D of the CAA and EPA's regulations because
Indiana's February 28, 2017, nonattainment plan submission and January
1, 2018, supplement satisfy the emissions inventory, RFP, RFP
contingency measures, transportation conformity, VOC RACT, I/M, and
nonattainment NSR requirements of the CAA for the Indiana portion of
the Chicago area for the 2008 ozone NAAQS. Final approval of Indiana's
SIP as meeting the nonattainment NSR requirements of the CAA for the
2008 ozone NAAQS will permanently stop the sanctions and FIP clocks
triggered by EPA's February 3, 2017 finding that Indiana failed to
submit a marginal ozone nonattainment NSR plan.
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 CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely 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);
[[Page 43836]]
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 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).
In addition, the SIP is not approved to apply on any Indian
reservation land or in any other area where EPA or an Indian tribe has
demonstrated that a tribe has jurisdiction. In those areas of Indian
country, the rule does not have tribal implications and will not impose
substantial direct costs on tribal governments or preempt tribal law as
specified by Executive Order 13175 (65 FR 67249, November 9, 2000).
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Intergovernmental relations, Ozone, Reporting and
recordkeeping requirements, Volatile organic compounds.
Dated: August 16, 2018.
Cathy Stepp,
Regional Administrator, Region 5.
[FR Doc. 2018-18640 Filed 8-27-18; 8:45 am]
BILLING CODE 6560-50-P