[Federal Register Volume 85, Number 172 (Thursday, September 3, 2020)]
[Proposed Rules]
[Pages 54961-54967]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-18394]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 52

[EPA-R03-OAR-2020-0316; FRL-10013-55-Region 3]


Air Plan Approval; Pennsylvania; 1997 8-Hour Ozone National 
Ambient Air Quality Standards Second Maintenance Plan for the Scranton-
Wilkes-Barre Area

AGENCY: Environmental Protection Agency (EPA).

ACTION: Proposed rule.

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SUMMARY: The Environmental Protection Agency (EPA) is proposing to 
approve a state implementation plan (SIP) revision submitted by the 
Commonwealth of Pennsylvania. This revision pertains to the 
Commonwealth's plan, submitted by the Pennsylvania Department of 
Environmental Protection (DEP), for maintaining the 1997 8-hour ozone 
national ambient air quality standard (NAAQS) (referred to as the 
``1997 ozone NAAQS'') in the Scranton-Wilkes-Barre, Pennsylvania area 
(Scranton-Wilkes-Barre Area). This action is being taken under the 
Clean Air Act (CAA).

DATES: Written comments must be received on or before October 5, 2020.

ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R03-
OAR-2020-0316 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

[[Page 54962]]

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://www.epa.gov/dockets/commenting-epa-dockets.

FOR FURTHER INFORMATION CONTACT: Maria A. Pino, Planning & 
Implementation Branch (3AD30), Air & Radiation Division, U.S. 
Environmental Protection Agency, Region III, 1650 Arch Street, 
Philadelphia, Pennsylvania 19103. The telephone number is (215) 814-
2181. Ms. Pino can also be reached via electronic mail at 
[email protected].

SUPPLEMENTARY INFORMATION: On March 10, 2020, DEP submitted a revision 
to the Pennsylvania SIP to incorporate a plan for maintaining the 1997 
ozone NAAQS in the Scranton-Wilkes-Barre Area through December 19, 
2027, in accordance with CAA section 175A.

I. Background

    In 1979, under section 109 of the CAA, EPA established primary and 
secondary NAAQS for ozone at 0.12 parts per million (ppm), averaged 
over a 1-hour period. 44 FR 8202 (February 8, 1979). On July 18, 1997 
(62 FR 38856),\1\ EPA revised the primary and secondary NAAQS for ozone 
to set the acceptable level of ozone in the ambient air at 0.08 ppm, 
averaged over an 8-hour period. EPA set the 1997 ozone NAAQS based on 
scientific evidence demonstrating that ozone causes adverse health 
effects at lower concentrations and over longer periods of time than 
was understood when the pre-existing 1-hour ozone NAAQS was set.
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    \1\ In March 2008, EPA completed another review of the primary 
and secondary ozone standards and tightened them further by lowering 
the level for both to 0.075 ppm. 73 FR 16436 (March 27, 2008). 
Additionally, in October 2015, EPA completed a review of the primary 
and secondary ozone standards and tightened them by lowering the 
level for both to 0.70 ppm. 80 FR 65292 (October 26, 2015).
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    Following promulgation of a new or revised NAAQS, EPA is required 
by the CAA to designate areas throughout the nation as attaining or not 
attaining the NAAQS. On April 30, 2004 (69 FR 23858), EPA designated 
the Scranton-Wilkes-Barre Area as nonattainment for the 1997 ozone 
NAAQS. The Scranton-Wilkes-Barre Area consists of Lackawanna, Luzerne, 
Monroe, and Wyoming counties in Pennsylvania.
    Once a nonattainment area has three years of complete and certified 
air quality data that has been determined to attain the NAAQS, and the 
area has met the other criteria outlined in CAA section 
107(d)(3)(E),\2\ the state can submit a request to EPA to redesignate 
the area to attainment. Areas that have been redesignated by EPA from 
nonattainment to attainment are referred to as ``maintenance areas.'' 
One of the criteria for redesignation is to have an approved 
maintenance plan under CAA section 175A. The maintenance plan must 
demonstrate that the area will continue to maintain the standard for 
the period extending 10 years after redesignation, and it must contain 
such additional measures as necessary to ensure maintenance as well as 
contingency measures as necessary to assure that violations of the 
standard will be promptly corrected.
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    \2\ The requirements of CAA section 107(d)(3)(E) include 
attainment of the NAAQS, full approval under section 110(k) of the 
applicable SIP, determination that improvement in air quality is a 
result of permanent and enforceable reductions in emissions, 
demonstration that the state has met all applicable section 110 and 
part D requirements, and a fully approved maintenance plan under CAA 
section 175A.
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    On November 19, 2007 (72 FR 64948 effective December 19, 2007), EPA 
approved a redesignation request (and maintenance plan) from DEP for 
the Scranton-Wilkes-Barre Area. In accordance with section 175A(b), at 
the end of the eighth year after the effective date of the 
redesignation, the state must also submit a second maintenance plan to 
ensure ongoing maintenance of the standard for an additional 10 years.
    EPA's final implementation rule for the 2008 ozone NAAQS revoked 
the 1997 ozone NAAQS and provided that one consequence of revocation 
was that areas that had been redesignated to attainment (i.e., 
maintenance areas) for the 1997 ozone NAAQS no longer needed to submit 
second 10-year maintenance plans under CAA section 175A(b).\3\ However, 
in South Coast Air Quality Management District v. EPA \4\ (South Coast 
II), the United States Court of Appeals for the District of Columbia 
(D.C. Circuit) vacated EPA's interpretation that, because of the 
revocation of the 1997 ozone standard, second maintenance plans were 
not required for ``orphan maintenance areas,'' (i.e., areas like the 
Scranton-Wilkes-Barre Area) that had been redesignated to attainment 
for the 1997 ozone NAAQS and were designated attainment for the 2008 
ozone NAAQS. Thus, states with these ``orphan maintenance areas'' under 
the 1997 ozone NAAQS must submit maintenance plans for the second 
maintenance period.
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    \3\ See 80 FR 12315 (March 6, 2015).
    \4\ 882 F.3d 1138 (D.C. Cir. 2018).
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    As previously discussed, CAA section 175A sets forth the criteria 
for adequate maintenance plans. In addition, EPA has published 
longstanding guidance that provides further insight on the content of 
an approvable maintenance plan, explaining that a maintenance plan 
should address five elements: (1) An attainment emissions inventory; 
(2) a maintenance demonstration; (3) a commitment for continued air 
quality monitoring; (4) a process for verification of continued 
attainment; and (5) a contingency plan. The 1992 Calcagni Memo \5\ 
provides that states may generally demonstrate maintenance by either 
performing air quality modeling to show that the future mix of sources 
and emission rates will not cause a violation of the NAAQS or by 
showing that future emissions of a pollutant and its precursors will 
not exceed the level of emissions during a year when the area was 
attaining the NAAQS (i.e., attainment year inventory). See 1992 
Calcagni Memo at p. 9. EPA further clarified in three subsequent 
guidance memos describing ``limited maintenance plans'' (LMPs) \6\ that 
the requirements of CAA section 175A could be met by demonstrating that 
the area's design value \7\ was well below the NAAQS and

[[Page 54963]]

that the historical stability of the area's air quality levels showed 
that the area was unlikely to violate the NAAQS in the future. 
Specifically, EPA believes that if the most recent air quality design 
value for the area is at a level that is below 85% of the standard, or 
in this case below 0.071 ppm, then EPA considers the state to have met 
the section 175A requirement for a demonstration that the area will 
maintain the NAAQS for the requisite period. Accordingly, on March 10, 
2020, DEP submitted an LMP for the Scranton-Wilkes-Barre Area, 
following EPA's LMP guidance and demonstrating that the area will 
maintain the 1997 ozone NAAQS through December 19, 2027, i.e., through 
the entire 20-year maintenance period.
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    \5\ ``Procedures for Processing Requests to Redesignate Areas to 
Attainment,'' Memorandum from John Calcagni, Director, Air Quality 
Management Division, September 4, 1992 (1992 Calcagni Memo).
    \6\ See ``Limited Maintenance Plan Option for Nonclassifiable 
Ozone Nonattainment Areas'' from Sally L. Shaver, Office of Air 
Quality Planning and Standards (OAQPS), dated November 16, 1994; 
``Limited Maintenance Plan Option for Nonclassifiable CO 
Nonattainment Areas'' from Joseph Paisie, OAQPS, dated October 6, 
1995; and ``Limited Maintenance Plan Option for Moderate 
PM10 Nonattainment Areas'' from Lydia Wegman, OAQPS, 
dated August 9, 2001.
    \7\ The ozone design value for a monitoring site is the 3-year 
average of the annual fourth-highest daily maximum 8-hour average 
ozone concentrations. The design value for an ozone nonattainment 
area is the highest design value of any monitoring site in the area.
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II. Summary of SIP Revision and EPA Analysis

    DEP's March 10, 2020 SIP submittal outlines a plan for continued 
maintenance of the 1997 ozone NAAQS which addresses the criteria set 
forth in the 1992 Calcagni Memo as follows.

A. Attainment Emissions Inventory

    For maintenance plans, a state should develop a comprehensive and 
accurate inventory of actual emissions for an attainment year which 
identifies the level of emissions in the area which is sufficient to 
maintain the NAAQS. The inventory should be developed consistent with 
EPA's most recent guidance. For ozone, the inventory should be based on 
typical summer day's emissions of oxides of nitrogen (NOX) 
and volatile organic compounds (VOC), the precursors to ozone 
formation. In the first maintenance plan for the Scranton-Wilkes-Barre 
Area, DEP used 2004 for the attainment year inventory, because 2004 was 
one of the years in the 2004-2006 three-year period when the area first 
attained the 1997 ozone NAAQS.\8\ The Scranton-Wilkes-Barre Area 
continued to monitor attainment of the 1997 ozone NAAQS in 2014. 
Therefore, the emissions inventory from 2014 represents emissions 
levels conducive to continued attainment (i.e., maintenance) of the 
NAAQS. Thus, DEP is using 2014 as representing attainment level 
emissions for its second maintenance plan. Pennsylvania used 2014 
summer day emissions from EPA's 2014 version 7.0 modeling platform as 
the basis for the 2014 inventory presented in Table 1.\9\
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    \8\ For more information, see EPA's September 25, 2007 notice 
proposing to redesignate the Scranton-Wilkes-Barre Area to 
attainment for the 1997 ozone NAAQS (72 FR 54390).
    \9\ For more information, visit https://www.epa.gov/sites/production/files/2018-11/ozone_1997_naaqs_emiss_inv_data_nov_19_2018_0.xlsx.

            Table 1--2014 Typical Summer Day NOX and VOC Emissions for the Scranton-Wilkes-Barre Area
                                                   [Tons/day]
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                                                                                  NOX  emissions
                    County                               Source category                          VOC  emissions
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Lackawanna....................................  Point...........................            0.71            0.46
                                                Nonpoint........................            2.89            9.33
                                                Onroad..........................            8.96            3.72
                                                Nonroad.........................            1.14            1.51
Luzerne.......................................  Point...........................            1.12            0.95
                                                Nonpoint........................            3.93           15.10
                                                Onroad..........................           15.62            6.15
                                                Nonroad.........................            2.32            4.24
Monroe........................................  Point...........................            0.13            0.13
                                                Nonpoint........................            1.18            5.84
                                                Onroad..........................            9.63            4.06
                                                Nonroad.........................            1.78            5.08
Wyoming.......................................  Point...........................            1.56            0.49
                                                Nonpoint........................            2.64            7.21
                                                Onroad..........................            1.73            0.75
                                                Nonroad.........................            0.52            1.96
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    The data shown in Table 1 is based on the 2014 National Emissions 
Inventory (NEI) version 2.\10\ The inventory addresses four 
anthropogenic emission source categories: Stationary (point) sources, 
stationary nonpoint (area) sources, nonroad mobile, and onroad mobile 
sources. Point sources are stationary sources that have the potential 
to emit (PTE) more than 100 tons per year (tpy) of VOC, or more than 50 
tpy of NOX, and which are required to obtain an operating 
permit. Data are collected for each source at a facility and reported 
to DEP. Examples of point sources include kraft mills, electrical 
generating units (EGUs), and pharmaceutical factories. Nonpoint sources 
include emissions from equipment, operations, and activities that are 
numerous and in total have significant emissions. Examples include 
emissions from commercial and consumer products, portable fuel 
containers, home heating, repair and refinishing operations, and 
crematories. The onroad emissions sector includes emissions from 
engines used primarily to propel equipment on highways and other roads, 
including passenger vehicles, motorcycles, and heavy-duty diesel 
trucks. The nonroad emissions sector includes emissions from engines 
that are not primarily used to propel transportation equipment, such as 
generators, forklifts, and marine pleasure craft.
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    \10\ The NEI is a comprehensive and detailed estimate of air 
emissions of criteria pollutants, criteria precursors, and hazardous 
air pollutants from air emissions sources. The NEI is released every 
three years based primarily upon data provided by State, Local, and 
Tribal air agencies for sources in their jurisdictions and 
supplemented by data developed by EPA.
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    EPA reviewed the emissions inventory submitted by DEP and proposes 
to conclude that the plan's inventory is acceptable for the purposes of 
a subsequent maintenance plan under CAA section 175A(b).

B. Maintenance Demonstration

    In order to attain the 1997 ozone NAAQS, the three-year average of 
the fourth-highest daily average ozone concentrations (design value, or 
``DV'') at each monitor within an area must not exceed 0.08 ppm. Based 
on the rounding convention described in 40 CFR part 50, appendix I, the 
standard is

[[Page 54964]]

attained if the DV is 0.084 or below. CAA section 175A requires a 
demonstration that the area will continue to maintain the NAAQS 
throughout the duration of the requisite maintenance period. Consistent 
with the prior guidance documents discussed previously in this document 
as well as EPA's November 20, 2018 ``Resource Document for 1997 Ozone 
NAAQS Areas: Supporting Information for States Developing Maintenance 
Plans'' (2018 Resource Document),\11\ EPA believes that if the most 
recent DV for the area is well below the NAAQS (e.g., below 85%, or in 
this case below 0.071 ppm), the section 175A demonstration requirement 
has been met, provided that Prevention of Significant Deterioration 
(PSD) requirements, any control measures already in the SIP, and any 
Federal measures remain in place through the end of the second 10-year 
maintenance period (absent a showing consistent with section 110(l) 
that such measures are not necessary to assure maintenance).
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    \11\ This resource document is included in the docket for this 
rulemaking available online at https://www.regulations.gov, Docket 
ID: EPA-R03-OAR-2020-0316 and is also available at https://www.epa.gov/sites/production/files/2018-11/documents/ozone_1997_naaqs_lmp_resource_document_nov_20_2018.pdf.
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    For the purposes of demonstrating continued maintenance with the 
1997 ozone NAAQS, DEP provided 3-year DVs at monitors located in the 
Scranton-Wilkes-Barre Area from 2007 to 2018. This includes DVs at 
monitors for 2005-2007, 2006-2008, 2007-2009, 2008-2010, 2009-2011, 
2010-2012, 2011-2013, 2012-2014, 2013-2015, 2014-2016, 2015-2017, and 
2016-2018, which are shown in Table 2.\12\ In addition, EPA has 
reviewed the most recent ambient air quality monitoring data for ozone 
in the Scranton-Wilkes-Barre Area, as submitted by Pennsylvania and 
recorded in EPA's Air Quality System (AQS). The most recent DVs (i.e., 
2017-2019) at monitors located in the Scranton-Wilkes-Barre Area are 
also shown in Table 2.\13\
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    \12\ See also Table II-2 of DEP's March 10, 2020 submittal, 
included in the docket for this rulemaking available online at 
https://www.regulations.gov, Docket ID: EPA-R03-OAR-2020-0316.
    \13\ This data is also included in the docket for this 
rulemaking available online at https://www.regulations.gov, Docket 
ID: EPA-R03-OAR-2020-0316 and is also available at https://www.epa.gov/air-trends/air-quality-design-values#report.

                                                           Table 2--1997 Ozone NAAQS Design Values for the Scranton-Wilkes-Barre Area
                                                                                    [Parts per million [ppm]]
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              County                 AQS site ID   2005-2007  2006-2008  2007-2009  2008-2010  2009-2011  2010-2012  2011-2013  2012-2014  2013-2015  2014-2016  2015-2017  2016-2018  2017-2019
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Lackawanna.......................     42-069-0101      .074       .072       .071       .072       .071       .072       .070       .066       .065       .067       .067       .064       .059
Lackawanna \a\...................     42-069-2006      .075       .074       .071       .069       .066       .071       .069   .........  .........  .........      .064       .061       .060
Luzerne \b\......................     42-079-1100      .067       .067       .066       .069       .065       .066       .064   .........  .........  .........  .........  .........  .........
Luzerne..........................     42-079-1101      .076       .075       .069       .065       .062       .066       .065       .063       .063       .064       .064       .064       .062
Monroe \c\.......................     42-089-0002     (\a\)       .076       .069       .070       .066       .070       .064       .063       .063       .065       .067       .068       .065
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\a\ This monitor (AQS Site ID 42-069-2006) was relocated and shut down from March 2014 to July 2014. The relocation and resulting shutdown of the monitor caused incomplete data for 2014, which
  is why there are no design values listed for 2012-2014, 2013-2015, and 2014-2016.
\b\ This monitor (AQS Site ID 42-079-1100) was discontinued on July 1, 2014. Therefore, there are no design values after 2011-2013.
\c\ The monitor located in Monroe County (AQS Site ID 42-089-002) began operation in April 2006, therefore, the first valid design value is for 2006-2008.

    As can be seen in Table 2, DVs at all monitors located in the 
Scranton-Wilkes-Barre Area have been well below 85% of the 1997 ozone 
NAAQS (i.e., 0.071 ppm) since the 2011-2013 period. The highest DV for 
the 2017-2019 period at a monitor in the Scranton-Wilkes-Barre Area is 
0.065 ppm, which is well below 85% of the 1997 ozone NAAQS.
    Additionally, states can support the demonstration of continued 
maintenance by showing stable or improving air quality trends. 
According to EPA's 2018 Resource Document, several kinds of analyses 
can be performed by states wishing to make such a showing. One approach 
is to take the most recent DV at a monitor located in the area and add 
the maximum design value increase (over one or more consecutive years) 
that has been observed in the area over the past several years. For an 
area with multiple monitors, the highest of the most recent DVs should 
be used. A sum that does not exceed the level of the 1997 ozone NAAQS 
may be a good indicator of expected continued attainment. As shown in 
Table 2, the largest increase in DVs at a monitor located in the 
Scranton-Wilkes-Barre Area was 0.005 ppm, which occurred between the 
2009-2011 (0.066 ppm) and 2010-2012 (0.071 ppm) DVs at the monitor 
located in Lackawanna County (AQS ID 42-069-2006). Adding 0.005 ppm to 
the highest DV for the 2017-2019 period (0.065 ppm) results in 0.070 
ppm, a sum that is still below the 1997 ozone NAAQS.
    The Scranton-Wilkes-Barre Area has maintained air quality levels 
well below the 1997 ozone NAAQS since the Area first attained the NAAQS 
in 2006.\14\ Additional supporting information that the area is 
expected to continue to maintain the standard can be found in 
projections of future year DVs that EPA recently completed to assist 
states with the development of interstate transport SIPs for the 2015 
8-hour ozone NAAQS. Those projections, made for the year 2023, show 
that the highest DV at a monitor located in the Scranton-Wilkes-Barre 
Area is expected to be 0.0558 ppm.\15\ Therefore, EPA proposes to 
determine that future violations of the 1997 ozone NAAQS in the 
Scranton-Wilkes-Barre Area are unlikely.
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    \14\ As explained in EPA's September 25, 2007 notice proposing 
to redesignate the Scranton-Wilkes-Barre Area as attainment for the 
1997 ozone NAAQS (72 FR 54390), the 2004-2006 DV for the Scranton-
Wilkes-Barre Area was 0.075 ppm.
    \15\ See U.S. EPA, ``Air Quality Modeling Technical Support 
Document for the Updated 2023 Projected Ozone Design Values'', 
Office of Air Quality Planning and Standards, dated June 2018, 
available at https://www.epa.gov/airmarkets/air-quality-modeling-technical-support-document-updated-2023-projected-ozone-design.
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C. Continued Air Quality Monitoring and Verification of Continued 
Attainment

    Once an area has been redesignated to attainment, the state remains 
obligated to maintain an air quality network in accordance with 40 CFR 
part 58, in order to verify the area's attainment status. In the March 
10, 2020 submittal, DEP commits to continue to operate their air 
monitoring network in accordance with 40 CFR part 58. DEP also commits 
to track the attainment status of the Scranton-Wilkes-Barre Area for 
the 1997 ozone NAAQS through the review of air quality and emissions 
data during the second maintenance period. This includes an annual 
evaluation of vehicles miles traveled (VMT) and stationary source 
emissions data compared to the assumptions included in the LMP. DEP 
also states that it will evaluate the periodic (i.e., every three

[[Page 54965]]

years) emission inventories prepared under EPA's Air Emission Reporting 
Requirements (40 CFR part 51, subpart A). Based on these evaluations, 
DEP will consider whether any further emission control measures should 
be implemented for the Scranton-Wilkes-Barre Area. EPA has analyzed the 
commitments in DEP's submittal and is proposing to determine that they 
meet the requirements for continued air quality monitoring and 
verification of continued attainment.

D. Contingency Plan

    The contingency plan provisions are designed to promptly correct or 
prevent a violation of the NAAQS that might occur after redesignation 
of an area to attainment. Section 175A of the CAA requires that a 
maintenance plan include such contingency measures as EPA deems 
necessary to assure that the state will promptly correct a violation of 
the NAAQS that occurs after redesignation. The maintenance plan should 
identify the contingency measures to be adopted, a schedule and 
procedure for adoption and implementation of the contingency measures, 
and a time limit for action by the state. The state should also 
identify specific indicators to be used to determine when the 
contingency measures need to be adopted and implemented. The 
maintenance plan must require that the state will implement all 
pollution control measures that were contained in the SIP before 
redesignation of the area to attainment. See section 175(A)(d) of the 
CAA.
    DEP's March 10, 2020 submittal includes a contingency plan for the 
Scranton-Wilkes-Barre Area. In the event that the fourth highest eight-
hour ozone concentrations at a monitor in the Scranton-Wilkes-Barre 
Area exceeds 84 ppb (equivalent to 0.084 ppm) for two consecutive 
years, but prior to an actual violation of the NAAQS, DEP will evaluate 
whether additional local emission control measures should be 
implemented that may prevent a violation of the NAAQS.\16\ After 
analyzing the conditions causing the excessive ozone levels, evaluating 
the effectiveness of potential corrective measures, and considering the 
potential effects of federal, state, and local measures that have been 
adopted but not yet implemented, DEP will begin the process of 
implementing selected measures so that they can be implemented as 
expeditiously as practicable following a violation of the NAAQS. In the 
event of a violation, DEP commits to adopting additional emission 
reduction measures as expeditiously as practicable in accordance with 
the schedule included in the contingency plan as well as the CAA and 
applicable Pennsylvania statutory requirements.
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    \16\ A violation of the NAAQS occurs when an area's 3-year 
design value exceeds the NAAQS.
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    DEP will use the following criteria when considering additional 
emission reduction measures to adopt to address a violation of the 1997 
ozone NAAQS in the Scranton-Wilkes-Barre Area: (1) Air quality analysis 
indicating the nature of the violation, including the cause, location, 
and source; (2) emission reduction potential, including extent to which 
emission generating sources occur in the nonattainment area; (3) 
timeliness of implementation in terms of the potential to return the 
area to attainment as expeditiously as practicable; and (4) costs, 
equity, and cost-effectiveness. The measures DEP would consider 
pursuing for adoption in the Scranton-Wilkes-Barre Area include, but 
are not limited to, those summarized in Table 3. If additional emission 
reductions are necessary, DEP commits to adopt additional emission 
reduction measures to attain and maintain the 1997 ozone NAAQS.

 Table 3--Scranton-Wilkes-Barre Area Second Maintenance Plan Contingency
                                Measures
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Non-Regulatory Measures:
    Voluntary diesel engine ``chip reflash'' (installation software to
     correct the defeat device option on certain heavy-duty diesel
     engines).
    Diesel retrofit (including replacement, repowering or alternative
     fuel use) for public or private local onroad or offroad fleets.
    Idling reduction technology for Class 2 yard locomotives.
    Idling reduction technologies or strategies for truck stops,
     warehouses, and other freight-handling facilities.
    Accelerated turnover of lawn and garden equipment, especially
     commercial equipment, including promotion of electric equipment.
    Additional promotion of alternative fuel (e.g., biodiesel) for home
     heating and agricultural use.
Regulatory Measures: \17\
    Additional control on consumer products.\18\
    Additional controls on portable fuel containers.\19\
------------------------------------------------------------------------

    The contingency plan includes schedules for the adoption and 
implementation of both non-regulatory and regulatory contingency 
measures, including schedules for adopting potential land use planning 
strategies not listed in Table 3, which are summarized in Tables 4 and 
5, respectively.
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    \17\ These regulatory measures were considered potential cost-
effective and timely control strategies by the Ozone Transport 
Commission (OTC) as well as the Mid-Atlantic Regional Air Management 
Association and the Mid-Atlantic/Northeast Visibility Union. The OTC 
is a multi-state organization responsible for developing regional 
solutions to ground-level ozone pollution in the Northeast and Mid-
Atlantic, including the development of model rules that member 
states may adopt. OTC member states include: Connecticut, Delaware, 
the District of Columbia, Maine, Maryland, Massachusetts, New 
Hampshire, New Jersey, New York, Pennsylvania, Rhode Island, 
Vermont, and Virginia. For more information on the OTC, visit 
https://otcair.org/index.asp. To view the model rules developed by 
the OTC, including those for consumer products and portable fuel 
containers, visit https://otcair.org/document.asp?fview=modelrules.
    \18\ Pennsylvania's existing controls on consumer products are 
under 25 Pa. Code Chapter 130, Subchapters B and C (38 Pa.B. 5598). 
This contingency measure includes the adoption of additional 
controls on consumer products such as VOC limits for adhesive 
removers.
    \19\ Existing controls on portable fuel containers can be found 
under 40 CFR part 59, subpart F--Control of Evaporative Emissions 
From New and In-Use Portable Fuel Containers.

  Table 4--Implementation Schedule for Scranton-Wilkes-Barre Area Non-
                     Regulatory Contingency Measures
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    Time after triggering event                    Action
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Within 2 months...................  DEP will identify stakeholders for
                                     potential non-regulatory measures
                                     for further development.
Within 3 months...................  If funding is necessary, DEP will
                                     identify potential sources of
                                     funding and the timeframe for when
                                     funds would be available.

[[Page 54966]]

 
Within 6 months...................  DEP will work with the relevant
                                     planning commission(s) to identify
                                     potential land use planning
                                     strategies and projects with
                                     quantifiable and timely emission
                                     benefits. DEP will also work with
                                     the Pennsylvania Department of
                                     Community and Economic Development
                                     and other state agencies to assist
                                     with these measures.
Within 9 months...................  If state loans or grants are
                                     required, DEP will enter into
                                     agreements with implementing
                                     organizations. DEP will also
                                     quantify projected emission
                                     benefits.
Within 12 months..................  DEP will submit revised SIP to EPA.
Within 12-24 months...............  DEP will implement strategies and
                                     projects.
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     Table 5--Implementation Schedule for Scranton-Wilkes-Barre Area
                     Regulatory Contingency Measures
------------------------------------------------------------------------
    Time after triggering event                    Action
------------------------------------------------------------------------
Within 1 month....................  DEP will submit request to begin
                                     regulatory development process.
Within 3 months...................  Request will be reviewed by the Air
                                     Quality Technical Advisory
                                     Committee (AQTAC), Citizens
                                     Advisory Council, and other
                                     advisory committees as appropriate.
Within 6 months...................  Environmental Quality Board (EQB)
                                     meeting/action.
Within 8 months...................  DEP will publish regulatory measure
                                     in the Pennsylvania Bulletin for
                                     comment as proposed rulemaking.
Within 10 months..................  DEP will hold a public hearing and
                                     comment period on proposed
                                     rulemaking.
Within 11 months..................  House and Senate Standing Committee
                                     and Independent Regulatory Review
                                     Commission (IRCC) comment on
                                     proposed rule.
Within 13 months..................  AQTAC, Citizens Advisory Council,
                                     and other committees will review
                                     responses to comment(s), if
                                     applicable, and the draft final
                                     rulemaking.
Within 16 months..................  EQB meeting/action.
Within 17 months..................  The IRCC will take action on final
                                     rulemaking.
Within 18 months..................  Attorney General's review/action.
Within 19 months..................  DEP will publish the regulatory
                                     measure as a final rulemaking in
                                     the Pennsylvania Bulletin and
                                     submit to EPA as a SIP revision.
                                     The regulation will become
                                     effective upon publication in the
                                     Pennsylvania Bulletin.
------------------------------------------------------------------------

    EPA proposes to find that the contingency plan included in DEP's 
March 10, 2020 submittal satisfies the pertinent requirements of CAA 
section 175A(d). EPA notes that while six of the potential contingency 
measures included in the Commonwealth's second maintenance plan are 
non-regulatory, their inclusion among other measures is overall SIP-
strengthening, and their inclusion does not alter EPA's proposal to 
find the LMP is fully approvable. EPA also finds that the submittal 
acknowledges Pennsylvania's continuing requirement to implement all 
pollution control measures that were contained in the SIP before 
redesignation of the Scranton-Wilkes-Barre Area to attainment.

E. Transportation Conformity

    Transportation conformity is required by section 176(c) of the CAA. 
Conformity to a SIP means that transportation activities will not 
produce new air quality violations, worsen existing violations, or 
delay timely attainment of the NAAQS (CAA 176(c)(1)(B)). EPA's 
conformity rule at 40 CFR part 93 requires that transportation plans, 
programs and projects conform to SIPs and establish the criteria and 
procedures for determining whether or not they conform. The conformity 
rule generally requires a demonstration that emissions from the 
Regional Transportation Plan (RTP) and Transportation Improvement 
Program (TIP) are consistent with the motor vehicle emissions budget 
(MVEB) contained in the control strategy SIP revision or maintenance 
plan (40 CFR 93.101, 93.118, and 93.124). A MVEB is defined as ``that 
portion of the total allowable emissions defined in the submitted or 
approved control strategy implementation plan revision or maintenance 
plan for a certain date for the purpose of meeting reasonable further 
progress milestones or demonstrating attainment or maintenance of the 
NAAQS, for any criteria pollutant or its precursors, allocated to 
highway and transit vehicle use and emissions (40 CFR 93.101).''
    Under the conformity rule, LMP areas may demonstrate conformity 
without a regional emission analysis (40 CFR 93.109(e)). However, 
because LMP areas are still maintenance areas, certain aspects of 
transportation conformity determinations still will be required for 
transportation plans, programs, and projects. Specifically, for such 
determination, RTPs, TIPs, and transportation projects still will have 
to demonstrate that they are fiscally constrained (40 CFR 93.108), meet 
the criteria for consultation (40 CFR 93.105 and 93.112) and 
transportation control measure implementation in the conformity rule 
provisions (40 CFR 93.113). Additionally, conformity determinations for 
RTPs and TIPs must be determined no less frequently than every four 
years, and conformity of plan and TIP amendments and transportation 
projects is demonstrated in accordance with the timing requirements 
specified in 40 CFR 93.104. In addition, for projects to be approved, 
they must come from a currently conforming RTP and TIP (40 CFR 93.114 
and 93.115). The Scranton-Wilkes-Barre Area remains under the 
obligation to meet the applicable conformity requirements for the 1997 
ozone NAAQS.

III. Proposed Action

    EPA's review of DEP's March 10, 2020 submittal indicates that it 
meets all applicable CAA requirements, specifically the requirements of 
CAA section 175A. EPA is proposing to approve the second maintenance 
plan for the Scranton-Wilkes-Barre Area as a revision to the 
Pennsylvania SIP. EPA is soliciting public comments on the issues 
discussed in this document. These comments will be considered before 
taking final action.

[[Page 54967]]

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 proposed action:
     Is not a ``significant regulatory action'' subject to 
review by the Office of Management and Budget under Executive Orders 
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21, 
2011);
     Is not an Executive Order 13771 (82 FR 9339, February 2, 
2017) regulatory action because SIP approvals are exempted under 
Executive Order 12866.
     Does not impose an information collection burden under the 
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
     Is certified as not having a significant economic impact 
on a substantial number of small entities under the Regulatory 
Flexibility Act (5 U.S.C. 601 et seq.);
     Does not contain any unfunded mandate or significantly or 
uniquely affect small governments, as described in the Unfunded 
Mandates Reform Act of 1995 (Pub. L. 104-4);
     Does not have Federalism implications as specified in 
Executive Order 13132 (64 FR 43255, August 10, 1999);
     Is not an economically significant regulatory action based 
on health or safety risks subject to Executive Order 13045 (62 FR 
19885, April 23, 1997);
     Is not a significant regulatory action subject to 
Executive Order 13211 (66 FR 28355, May 22, 2001);
     Is not subject to requirements of section 12(d) of the 
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272 
note) because application of those requirements would be inconsistent 
with the 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, this proposed rule, proposing approval of 
Pennsylvania's second maintenance plan for the Scranton-Wilkes-Barre 
Area, does not have tribal implications as specified by Executive Order 
13175 (65 FR 67249, November 9, 2000), because the SIP is not approved 
to apply in Indian country located in the State, and EPA notes that it 
will not impose substantial direct costs on tribal governments or 
preempt tribal law.

List of Subjects in 40 CFR Part 52

    Environmental protection, Air pollution control, Incorporation by 
reference, Intergovernmental relations, Nitrogen dioxide, Ozone, 
Reporting and recordkeeping requirements, Volatile organic compounds.

    Dated: August 17, 2020.
Cosmo Servidio,
Regional Administrator, Region III.
[FR Doc. 2020-18394 Filed 9-2-20; 8:45 am]
BILLING CODE 6560-50-P