Approval of Source Specific Air Quality Implementation Plans; New Jersey, 10458-10461 [2019-04781]
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10458
Federal Register / Vol. 84, No. 55 / Thursday, March 21, 2019 / Proposed Rules
Authority: 49 U.S.C. 106(f), 106(g); 40103,
40113, 40120; E.O. 10854, 24 FR 9565, 3 CFR,
1959–1963 Comp., p. 389.
missile attacks. Alternative locations
were not considered because the
purpose is to protect Guam, which
requires the THAAD to be located in
Guam.
§ 73.72 Guam
The Proposal
The FAA is proposing an amendment
to title 14 Code of Federal Regulations
(14 CFR) part 73 to establish restricted
area R–7205 Guam, GU. The FAA is
proposing this action at the request of
the USMC. The proposed restricted area
is described below.
R–7205 would be established on the
northern tip of Guam and northwest of
Anderson Air Force Base (AFB) abutting
the Anderson AFB Class D. The
altitudes would be from 700 feet MSL to
19,000 feet MSL.
Regulatory Notices and Analyses
The FAA has determined that this
proposed regulation only involves an
established body of technical
regulations for which frequent and
routine amendments are necessary to
keep them operationally current. It,
therefore: (1) Is not a ‘‘significant
regulatory action’’ under Executive
Order 12866; (2) is not a ‘‘significant
rule’’ under Department of
Transportation (DOT) Regulatory
Policies and Procedures (44 FR 11034;
February 26, 1979); and (3) does not
warrant preparation of a regulatory
evaluation as the anticipated impact is
so minimal. Since this is a routine
matter that will only affect air traffic
procedures and air navigation, it is
certified that this proposed rule, when
promulgated, will not have a significant
economic impact on a substantial
number of small entities under the
criteria of the Regulatory Flexibility Act.
Environmental Review
List of Subjects in 14 CFR Part 73
Airspace, Prohibited areas, Restricted
areas.
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The Proposed Amendment
In consideration of the foregoing, the
Federal Aviation Administration
proposes to amend 14 CFR part 73 as
follows:
1. The authority citation for part 73
continues to read as follows:
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R–7205 Guam, GU [New]
Boundaries. Beginning at lat. 13°37′10″ N,
long. 144°51′58″ E; thence clockwise along
the 2.4-mile radius of point in space
coordinates at lat. 13°39′25″ N, long.
144°51′04″ E; to lat. 13°38′40″ N, long.
144°53′24″ E; thence counter-clockwise along
the 4.3-mile radius of Andersen AFB Class D
airspace; to the point of beginning, excluding
that airspace within R–7202 when active.
Designated altitudes. 700 feet MSL to
FL190.
Time of designation. Continuous.
Controlling Agency. FAA, Guam CERAP.
Using Agency. Commanding Officer, Task
Force Talon, Andersen AFB, Guam.
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Issued in Washington, DC, on March 6,
2019.
Scott M. Rosenbloom,
Acting Manager, Airspace Policy Group.
[FR Doc. 2019–04534 Filed 3–20–19; 8:45 am]
BILLING CODE 4910–13–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R02–OAR–2018–0817, FRL–9990–92–
Region 2]
Approval of Source Specific Air Quality
Implementation Plans; New Jersey
Environmental Protection
Agency.
ACTION: Proposed rule.
AGENCY:
The Environmental Protection
Agency (EPA) is proposing to approve a
revision to the New Jersey State
Implementation Plan (SIP) for the 2008
8-hour ozone National Ambient Air
Quality Standard in relation to a Source
Specific SIP for Gerdau Ameristeel in
Sayreville, New Jersey. On December 5,
2018, the New Jersey Department of
Environmental Protection approved an
administrative amendment reflecting
new ownership and name change to
Commercial Metals Company. The
control options in the Source Specific
SIP that address nitrogen oxide
Reasonably Available Control
Technology for the natural gas fired
billet reheat furnace remain the same
under the new ownership. The intended
effect of this SIP revision is for the
Sayreville facility to continue to operate
SUMMARY:
This proposal will be subject to an
environmental analysis in accordance
with FAA Order 1050.1F,
‘‘Environmental Impacts: Policies and
Procedures’’ prior to any FAA final
regulatory action.
PART 73—SPECIAL USE AIRSPACE
[Amended]
2. Section 73.72 is amended as
follows:
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under their facility specific maximum
allowable nitrogen oxide emission rate.
The affected source will not increase
hourly nitrogen oxide emissions,
therefore, the National Ambient Air
Quality Standards for ozone is
protected.
DATES: Comments must be received on
or before April 22, 2019.
ADDRESSES: Submit your comments,
identified by Docket ID number EPA–
R02–OAR–2018–0817, at https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Once submitted, comments cannot be
edited or withdrawn. The 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. The 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, such as
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:
Linda Longo, Air Programs Branch,
Environmental Protection Agency, 290
Broadway, 25th Floor, New York, New
York 10007–1866, (212) 637–3565, or by
email at longo.linda@epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Background
II. EPA’s Evaluation of New Jersey’s
Submittal
III. Proposed Action
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
I. Background
The Environmental Protection Agency
(EPA) proposes to approve revisions to
the New Jersey State Implementation
Plan (SIP) for attainment and
maintenance of the 2008 ozone National
Ambient Air Quality Standard
(NAAQS). Specifically, under New
Jersey Administrative Code, Title 7,
Chapter 27, Subchapter 19, ‘‘Control
and Prohibition of Air Pollution from
Oxides of Nitrogen’’ (N.J.A.C. 7:27–19).
The New Jersey Department of
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Environmental Protection (NJDEP)
reviewed and approved the facility
specific emission limit (FSEL) nitrogen
oxide (NOX) control plan and the
associated Reasonably Available Control
Technology (RACT) for the Gerdau
Ameristeel facility located in Sayreville,
New Jersey (Sayreville Facility). The
RACT for this SIP revision is the lowest
emission limitation economically
feasible for controlling NOX emissions
from the Sayreville Facility’s billet
reheat furnace (Sayerville BRF). The
Sayreville BRF is used to raise the
temperature of steel billets to the
required level for hot rolling.
Subchapter N.J.A.C. 7:27–19.13(a)(1),
‘‘Alternative and facility specific NOX
emission limits,’’ allows owners and
operators of major sources of NOX, upon
approval of the NJDEP, to obtain FSELs
for maximum allowable NOX emission
rates by submitting a NOX control plan
that meets the requirements of N.J.A.C.
7:27–19.13(b). Furthermore, Subchapter
N.J.A.C. 7:27–19.13(a)(3) allows
facilities that wish to continue to
operate under existing NOX control
plans that were approved prior to May
1, 2005 to make the request by
submitting an updated proposed NOX
control plan as required in N.J.A.C.
7:27–19.13. The Sayreville Facility
wishes to continue to operate under its
existing NOX control plan that was
approved by the State on March 15,
2005. A full summary is included in the
technical support document (TSD) that
is contained in EPA’s docket assigned to
this Federal Register notice.
Please note that on December 5, 2018,
the NJDEP approved an administrative
amendment reflecting new ownership
and name change of the Sayreville
Facility from Gerdau Ameristeel to
Commercial Metals Company. All
control options for the Sayreville BRF
and CAA permit limits (as approved by
the NJDEP in the March 2005 NOx
control plan) remain the same under the
new ownership as were under the
former owner Gerdau Ameristeel.
Ozone Requirements
In 1997, the EPA revised the healthbased NAAQS for 8-hour ozone, setting
it at 0.084 parts per million (ppm)
averaged over an 8-hour time frame. See
62 FR 38856 (July 18, 1997). The EPA
revised the 8-hour ozone standard twice
since 1997; in March 2008, the EPA
revised the standard to 0.075 ppm, and
in October 2015 the EPA revised it to
0.070 ppm while retaining the 2008
ozone indicators. See 73 FR 16436
(March 27, 2008); 80 FR 65292 (October
26, 2015). After the EPA establishes a
new or revised NAAQS, the Clean Air
Act (CAA) directs the EPA and the
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states to take steps to ensure that the
new or revised NAAQS are met. One of
the first steps, known as the initial area
designations, involves identifying areas
of the country that are not meeting the
new or revised NAAQS, as well as the
nearby areas that contain emissions
sources that contribute emissions to the
areas not meeting the NAAQS.
The entire state of New Jersey has
been designated as nonattainment since
the adoption of the 1997 8-hour ozone
NAAQS and is divided into two
nonattainment areas. The two
nonattainment areas in New Jersey are
Philadelphia-Wilmington-Atlantic City
(PA–NJ–MD–DE) and New YorkNorthern New Jersey-Long Island (NY–
NJ–CT). These areas are designated as
marginal nonattainment and as
moderate nonattainment, respectively,
for the newest 0.070 ppm 8-hour ozone
NAAQS.1 As such, New Jersey has
developed ozone SIPs to attain the
standards and will consider sourcespecific SIPs as necessary. A sourcespecific SIP is submitted by a facility to
request approval for source-specific
emission limitations, and if approved by
the state and the EPA, are incorporated
into the state’s ozone SIP.
RACT Requirements
RACT is defined as the lowest
emission limit that a source is capable
of meeting by the application of control
technology that is reasonably available
considering technological and economic
feasibility.2 CAA sections 172(c)(1),
182(b)(2) and 182(f) require
nonattainment areas that are designated
as moderate or above to adopt RACT.
The entire state of New Jersey is subject
to this requirement because (1) of the
nonattainment area designations for the
8-hour ozone standards (40 CFR 81.331),
and (2) the state of New Jersey is located
within the Ozone Transport Region
(OTR), a region in which the CAA
requires that state SIPs implement
RACT requirements. See CAA
§ 184(b)(1)(B).
On November 25, 1992 the EPA
published a supplement to the General
Preamble to Title I of the CAA
Amendments of 1990 to clarify
requirements for NOX, referred to as the
1 Classifications of these areas for the current and
previous ozone NAAQS can be found at 40 CFR
81.331.
2 The EPA has not generally prescribed RACT
requirements. As defined in ‘‘State Implementation
Plans; General Preamble for Proposed Rulemaking
on Approval of Plan Revisions for Nonattainment
Areas—Supplement (on Control Techniques
Guidelines),’’ RACT for a particular source is
determined on a case-by-case basis, considering the
technological and economic circumstances of the
individual source. See 44 FR 53761 September 17,
1979.
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NOX Supplement. See 57 FR 55620. The
NOX Supplement explains that the CAA
section 182(f), read in conjunction with
section 182(a)(2)(C) and other New
Source Review (NSR) related provisions
in section 182, require state NSR plans
to apply to major stationary sources of
NOX, the same requirements that govern
major stationary sources of VOC
emissions in ozone nonattainment areas
and in other areas located in OTR.
Section182(a)(2)(C) requires States to
adopt and submit revised NSR
regulations for all ozone nonattainment
areas classified as marginal or above.
In November 2005, the EPA published
the final rule that discusses the RACT
requirements for the 1997 8-hour ozone
standard and outlined the SIP
requirements and deadlines for various
areas designated as moderate
nonattainment. See 70 FR 71612
(November 29, 2005) (the ‘‘Phase 2
Rule’’).
On August 1, 2007, the NJDEP
finalized RACT revisions to its SIP to
address the 8-hour ozone NAAQS and
the EPA approved on May 15, 2009. See
‘‘RACT for the 8-hour Ozone NAAQS
and other Associated SIP Revisions for
the Fine Particulate Matter, Regional
Haze, and Transport of Air Pollution,’’
available at https://www.nj.gov/dep/
baqp/sip/8-hrRACT-Final.pdf and see
74 FR 22837. The NJDEP, taking a more
stringent approach, believes that
significantly higher costs are warranted
and should be considered reasonable
with respect to available technology
than were discussed in the Phase 2
Rule. Although no dollar amount is
suggested, the NJDEP identifies five
considerations it plans to apply to
sources when determining RACT:
(1) Past New Jersey costs for
retrofitting a given control;
(2) Average RACT cost (dollars per
tons reduced) for a control technology
and maximum RACT cost. Once a
reasonable number of sources in a
source category achieve a lower
emission level, other sources should do
the same;
(3) The seriousness of the Region’s
ozone air quality exceedance. For
nonattainment areas with higher ozone
levels, higher costs for controls are
reasonable;
(4) The seriousness of the need to
reduce transported air pollution. As an
OTR state, higher costs for RACT are
justified; and
(5) The NJDEP plan for addressing
economic feasibility in RACT rules.
The NJDEP’s intent is to specify RACT
at the lowest emission limit that a
reasonable number of similar facilities
had already successfully implemented
for each source category.
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II. The EPA’s Evaluation of New
Jersey’s Submittals
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Continue To Operate Under Existing
NOX Control Plan
N.J.A.C. 19.13(a)(3) sets forth
requirements for facilities that wish to
continue to operate under existing NOX
control plans that were approved prior
to May 1, 2005. The regulation requires
such facilities to submit updated
proposed NOX control plans to NJDEP
for review. Gerdau Ameristeel originally
submitted an FSEL NOX control plan for
a BRF (old BRF) at the Sayreville
Facility to NJDEP in 1995. In 2004, the
facility submitted to NJDEP a proposed
FSEL NOX control plan for a
replacement BRF; the new unit was
designed with 64 ultra-low NOX
burners. On March 15, 2005, the NJDEP
approved the NOX control plan by
authorizing Gerdau Ameristeel to
replace the old BRF with the ultra-low
NOX burners.
On October 4, 2016, the Gerdau
Ameristeel submitted an updated
proposed NOX control plan to NJDEP
requesting to continue to operate the
March 15, 2005 NOX control plan for the
Sayreville BRF that has 64 ultra-low
NOX burners and maximum allowable
NOX emission rate of 58.9 tons per year
(TPY). On March 20, 2018, the NJDEP
submitted to the EPA a proposal to
allow the continued use of the control
options as outlined in the State
approved Gerdau Ameristeel March 15,
2005 NOX control plan.
The Sayreville BRF has a heat input
rating of 172.8 million British Thermal
Units per hour (MMBTU/hr) and is
permitted under the facility’s CAA Title
V operating permit (i.e., PI 18052, BOP
150001) for no more than 0.1 MMBTU/
hr of NOX as a major source with FSEL
not to exceed 17.3 pounds NOX per hour
and 58.9 tons NOX per year. The
Sayreville Facility is required to
conduct annual emission testing to
demonstrate compliance with 0.1 lb/
MMBtu NOX emission rate limit. The
EPA has determined that the Sayreville
BRF identified in the SIP revision are
consistent with New Jersey’s NOX RACT
regulation and the EPA’s guidance.
RACT Analysis
The RACT analysis conducted by
Gerdau Ameristeel found eight control
technologies suitable for a typical BRF:
(1) Ultra-low NOX burners currently in
use at the facility, (2) low excess air
currently in use at the facility, (3)
selective catalytic reduction (SCR), (4)
Low NOX burners, (5) Flue gas
recirculation or reduction of air preheat
temperature, (6) Burners out of service,
(7) Selective non-catalytic reduction,
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and (8) Non-selective catalytic
reduction. Under the regulations, the
first three are technologically feasible,
but the latter four were not.
Although the SCR was determined to
be technologically feasible, the
Sayreville Facility has major concerns
with its implementation. First, the
facility would need to install an
evaporative cooler to control the
temperature of the exiting flu gas for
this technology to be effective. Second,
the SCR catalyst could become damaged
by the BRF process. The exhaust gas
from the BRF contains concentrations of
particulate matter, including metals,
which would cause catalyst plugging
and masking. The potential for damage
cannot be determined with certainty
because the Sayreville Facility does not
currently have SCR units installed on
any BRF that control NOX to compare
potential catalyst poisoning. Moreover,
to the best of our knowledge no BRFs in
the United States currently employs
SCR units.3
Cost analysis was conducted for those
control technologies found to be
technologically feasible. Since the ultralow NOX burners and the low excess air
control technologies are currently in use
on the facility’s BRF, Gerdau Ameristeel
conducted the cost effectiveness study
only for the SCR. The facility concludes
that to purchase and install the SCR will
cost $4,279,380 and the annual
operating cost would be $1,164,379
based on a 20-year useful life of the
BRF. The cost effectiveness is based on
the annual cost of operating SCR and
the amount of NOX that would be
removed. The amount NOX that would
be removed from the SCR is based on
90% (0.9) control efficiency not to
exceed the CAA Title V operating
permit limit of 58.9 NOX TPY (58.9 TPY
× 0.9 = 53 TPY). Therefore, the SCR
would result in 53 TPY NOX removed
making the cost effectiveness to be
$21,965 per ton NOX removed
($1,164,379 ÷ 53 = $21,965), which is
above the federal RACT guidance.
Under EPA guidance, states should
consider in their RACT determinations
technologies that achieve 30–50 percent
reduction within a cost range of $160–
$1,300 per ton of NOX removed. See 70
FR 71652.
The SCR control technology was
found not to be RACT due to
technological and economical
3 The EPA’s RACT/BACT/LEAR Clearinghouse
(RBLC), https://cfpub.epa.gov/rblc/index.cfm
?action=Home.Home&lang=en, demonstrates that 9
U.S. facilities operate a reheat furnace, including
billet reheat furnace, and have NOX emissions. All
9 facilities have pollution prevention add-on
control technologies ultra-low or low NOX burners
and none are equipped with SCR.
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infeasibility under federal and state
RACT criteria.
III. Proposed Action
Gerdau Ameristeel reached agreement
with the NJDEP to continue to operate
under the approved March 15, 2005
NOX control plan that allowed the
Sayreville BRF to operate using 64 ultralow NOX burners. The Sayreville
Facility underwent a change in
ownership to the Commercial Metals
Company without changing its
production process or associated
equipment. Moreover, the Sayreville
Facility met the regulatory requirements
under N.J.A.C. 19.13(a)(3) to submit and
obtain NJDEP approval for an updated
proposed NOX control plan requesting
to continue to operate under their 2005
NOX control plan approved prior to May
1, 2005. The updated NOX control plan
demonstrates that the only technically
feasible control technology currently not
in use on the Sayreville BRF is the SCR
option and concludes that it is not
RACT. Therefore, the EPA proposes to
approve the NJDEP SIP revisions for 8hour ozone for Commercial Metals
Company continuing to operate under
the 2005 NOX Control Plan.
IV. Incorporation by Reference
In this document, we are proposing to
include regulatory text in an EPA final
rule that includes incorporation by
reference. In accordance with
requirements of 1 CFR 51.5, we are
proposing to incorporate by reference
the provisions described above in
Section III. Proposed Action.
The EPA has made, and will continue
to make, these documents generally
available electronically through https://
www.regulations.gov and in hard copy
at the appropriate EPA office, 290
Broadway, 25th floor, New York, New
York, 10007–1866 (see the ADDRESSES
section of this preamble for more
information).
V. Statutory and Executive Order
Reviews
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely proposes to approve state law as
meeting Federal requirements and does
not impose additional requirements
beyond those imposed by state law. For
that reason, this proposed action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
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of Management and Budget under
Executive Order 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 (Public Law 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 does
not have tribal implications as specified
by Executive Order 13175, 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. Thus, Executive
Order 13175 does not apply to this
action.
List of Subjects 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Nitrogen Dioxide,
Intergovernmental Relations, Ozone,
Reporting and recordkeeping
requirements.
Authority: 42 U.S.C. 7401 et seq.
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Dated: March 9, 2019.
Peter D. Lopez,
Regional Administrator, Region 2.
[FR Doc. 2019–04781 Filed 3–20–19; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 81
[EPA–R05–OAR–2018–0842; FRL–9991–11–
Region 5]
Air Plan Approval; Illinois;
Redesignation of the Illinois Portion of
the St. Louis Area to Attainment of the
1997 Annual Standard for Fine
Particulate Matter
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
On December 6, 2018, the
Illinois Environmental Protection
Agency (Illinois) submitted a request for
the Environmental Protection Agency
(EPA) to redesignate the Illinois portion
of the St. Louis, MO–IL nonattainment
area (hereafter, ‘‘St. Louis area’’) to
attainment for the 1997 fine particulate
matter (PM2.5) annual national ambient
air quality standard (NAAQS or
standard). The Illinois portion of the St.
Louis area includes Madison, Monroe,
and St. Clair counties, and Baldwin
Township in Randolph County. EPA is
taking this action because it has
determined that the St. Louis area is
attaining the annual 1997 PM2.5
standard based on the most recent three
years of certified air quality data. EPA
is also proposing to approve a revision
to the Illinois state implementation plan
(SIP) for maintaining the 1997 annual
PM2.5 NAAQS through 2030. Illinois’
maintenance plan submission includes
an updated emission inventory, which
includes emission inventories for PM2.5,
NOX, volatile organic compounds
(VOCs) and ammonia. The maintenance
plan submission also includes motor
vehicle emission budgets (MVEBs) for
the mobile source contribution of PM2.5
and nitrogen oxides (NOX) to the St.
Louis PM2.5 area for transportation
conformity purposes. EPA is proposing
to approve and update both the
emissions inventory and MVEBs. EPA is
proposing to take these actions in
accordance with the Clean Air Act
(CAA) and EPA’s SIP rules regarding the
1997 PM2.5 NAAQS.
DATES: Comments must be received on
or before April 22, 2019.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2018–0842 at https://
SUMMARY:
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10461
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:
Michelle Becker, Life Scientist,
Attainment Planning and Maintenance
Section, Air Programs Branch (AR–18J),
Environmental Protection Agency,
Region 5, 77 West Jackson Boulevard,
Chicago, Illinois 60604, (312) 886–3901,
Becker.Michelle@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 actions are EPA taking?
II. What is the background for these actions?
III. What are the criteria for redesignation to
attainment?
IV. What is EPA’s analysis of the state’s
request?
1. Attainment Determination (Section
107(d)(3)(E)(i)).
2. Section 110 and Part D Requirements,
and Approval SIP under Section 110(k)
(Section 107(d)(3)(E)(ii) and (v)).
3. Permanent and Enforceable Reductions
in Emissions (Section 107(d)(3)(E)(iii)).
4. Maintenance Plan Pursuant to Section
175A of the CAA (Section
107(d)(3)(E)(iv)).
5. Motor Vehicle Emissions Budget
(MVEBs) for PM2.5 and NOX, and Safety
Margin for the St. Louis Area.
6. Comprehensive Emissions Inventory for
the St. Louis Area
V. What are the effects of EPA’s actions?
VI. Statutory and Executive Order Reviews.
E:\FR\FM\21MRP1.SGM
21MRP1
Agencies
[Federal Register Volume 84, Number 55 (Thursday, March 21, 2019)]
[Proposed Rules]
[Pages 10458-10461]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-04781]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R02-OAR-2018-0817, FRL-9990-92-Region 2]
Approval of Source Specific Air Quality Implementation Plans; New
Jersey
AGENCY: Environmental Protection Agency.
ACTION: Proposed rule.
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SUMMARY: The Environmental Protection Agency (EPA) is proposing to
approve a revision to the New Jersey State Implementation Plan (SIP)
for the 2008 8-hour ozone National Ambient Air Quality Standard in
relation to a Source Specific SIP for Gerdau Ameristeel in Sayreville,
New Jersey. On December 5, 2018, the New Jersey Department of
Environmental Protection approved an administrative amendment
reflecting new ownership and name change to Commercial Metals Company.
The control options in the Source Specific SIP that address nitrogen
oxide Reasonably Available Control Technology for the natural gas fired
billet reheat furnace remain the same under the new ownership. The
intended effect of this SIP revision is for the Sayreville facility to
continue to operate under their facility specific maximum allowable
nitrogen oxide emission rate. The affected source will not increase
hourly nitrogen oxide emissions, therefore, the National Ambient Air
Quality Standards for ozone is protected.
DATES: Comments must be received on or before April 22, 2019.
ADDRESSES: Submit your comments, identified by Docket ID number EPA-
R02-OAR-2018-0817, at https://www.regulations.gov. Follow the online
instructions for submitting comments. Once submitted, comments cannot
be edited or withdrawn. The 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. The 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, such as 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: Linda Longo, Air Programs Branch,
Environmental Protection Agency, 290 Broadway, 25th Floor, New York,
New York 10007-1866, (212) 637-3565, or by email at
longo.linda@epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Background
II. EPA's Evaluation of New Jersey's Submittal
III. Proposed Action
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
I. Background
The Environmental Protection Agency (EPA) proposes to approve
revisions to the New Jersey State Implementation Plan (SIP) for
attainment and maintenance of the 2008 ozone National Ambient Air
Quality Standard (NAAQS). Specifically, under New Jersey Administrative
Code, Title 7, Chapter 27, Subchapter 19, ``Control and Prohibition of
Air Pollution from Oxides of Nitrogen'' (N.J.A.C. 7:27-19). The New
Jersey Department of
[[Page 10459]]
Environmental Protection (NJDEP) reviewed and approved the facility
specific emission limit (FSEL) nitrogen oxide (NOX) control
plan and the associated Reasonably Available Control Technology (RACT)
for the Gerdau Ameristeel facility located in Sayreville, New Jersey
(Sayreville Facility). The RACT for this SIP revision is the lowest
emission limitation economically feasible for controlling
NOX emissions from the Sayreville Facility's billet reheat
furnace (Sayerville BRF). The Sayreville BRF is used to raise the
temperature of steel billets to the required level for hot rolling.
Subchapter N.J.A.C. 7:27-19.13(a)(1), ``Alternative and facility
specific NOX emission limits,'' allows owners and operators
of major sources of NOX, upon approval of the NJDEP, to
obtain FSELs for maximum allowable NOX emission rates by
submitting a NOX control plan that meets the requirements of
N.J.A.C. 7:27-19.13(b). Furthermore, Subchapter N.J.A.C. 7:27-
19.13(a)(3) allows facilities that wish to continue to operate under
existing NOX control plans that were approved prior to May
1, 2005 to make the request by submitting an updated proposed
NOX control plan as required in N.J.A.C. 7:27-19.13. The
Sayreville Facility wishes to continue to operate under its existing
NOX control plan that was approved by the State on March 15,
2005. A full summary is included in the technical support document
(TSD) that is contained in EPA's docket assigned to this Federal
Register notice.
Please note that on December 5, 2018, the NJDEP approved an
administrative amendment reflecting new ownership and name change of
the Sayreville Facility from Gerdau Ameristeel to Commercial Metals
Company. All control options for the Sayreville BRF and CAA permit
limits (as approved by the NJDEP in the March 2005 NOx
control plan) remain the same under the new ownership as were under the
former owner Gerdau Ameristeel.
Ozone Requirements
In 1997, the EPA revised the health-based NAAQS for 8-hour ozone,
setting it at 0.084 parts per million (ppm) averaged over an 8-hour
time frame. See 62 FR 38856 (July 18, 1997). The EPA revised the 8-hour
ozone standard twice since 1997; in March 2008, the EPA revised the
standard to 0.075 ppm, and in October 2015 the EPA revised it to 0.070
ppm while retaining the 2008 ozone indicators. See 73 FR 16436 (March
27, 2008); 80 FR 65292 (October 26, 2015). After the EPA establishes a
new or revised NAAQS, the Clean Air Act (CAA) directs the EPA and the
states to take steps to ensure that the new or revised NAAQS are met.
One of the first steps, known as the initial area designations,
involves identifying areas of the country that are not meeting the new
or revised NAAQS, as well as the nearby areas that contain emissions
sources that contribute emissions to the areas not meeting the NAAQS.
The entire state of New Jersey has been designated as nonattainment
since the adoption of the 1997 8-hour ozone NAAQS and is divided into
two nonattainment areas. The two nonattainment areas in New Jersey are
Philadelphia-Wilmington-Atlantic City (PA-NJ-MD-DE) and New York-
Northern New Jersey-Long Island (NY-NJ-CT). These areas are designated
as marginal nonattainment and as moderate nonattainment, respectively,
for the newest 0.070 ppm 8-hour ozone NAAQS.\1\ As such, New Jersey has
developed ozone SIPs to attain the standards and will consider source-
specific SIPs as necessary. A source-specific SIP is submitted by a
facility to request approval for source-specific emission limitations,
and if approved by the state and the EPA, are incorporated into the
state's ozone SIP.
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\1\ Classifications of these areas for the current and previous
ozone NAAQS can be found at 40 CFR 81.331.
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RACT Requirements
RACT is defined as the lowest emission limit that a source is
capable of meeting by the application of control technology that is
reasonably available considering technological and economic
feasibility.\2\ CAA sections 172(c)(1), 182(b)(2) and 182(f) require
nonattainment areas that are designated as moderate or above to adopt
RACT. The entire state of New Jersey is subject to this requirement
because (1) of the nonattainment area designations for the 8-hour ozone
standards (40 CFR 81.331), and (2) the state of New Jersey is located
within the Ozone Transport Region (OTR), a region in which the CAA
requires that state SIPs implement RACT requirements. See CAA Sec.
184(b)(1)(B).
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\2\ The EPA has not generally prescribed RACT requirements. As
defined in ``State Implementation Plans; General Preamble for
Proposed Rulemaking on Approval of Plan Revisions for Nonattainment
Areas--Supplement (on Control Techniques Guidelines),'' RACT for a
particular source is determined on a case-by-case basis, considering
the technological and economic circumstances of the individual
source. See 44 FR 53761 September 17, 1979.
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On November 25, 1992 the EPA published a supplement to the General
Preamble to Title I of the CAA Amendments of 1990 to clarify
requirements for NOX, referred to as the NOX
Supplement. See 57 FR 55620. The NOX Supplement explains
that the CAA section 182(f), read in conjunction with section
182(a)(2)(C) and other New Source Review (NSR) related provisions in
section 182, require state NSR plans to apply to major stationary
sources of NOX, the same requirements that govern major
stationary sources of VOC emissions in ozone nonattainment areas and in
other areas located in OTR. Section182(a)(2)(C) requires States to
adopt and submit revised NSR regulations for all ozone nonattainment
areas classified as marginal or above.
In November 2005, the EPA published the final rule that discusses
the RACT requirements for the 1997 8-hour ozone standard and outlined
the SIP requirements and deadlines for various areas designated as
moderate nonattainment. See 70 FR 71612 (November 29, 2005) (the
``Phase 2 Rule'').
On August 1, 2007, the NJDEP finalized RACT revisions to its SIP to
address the 8-hour ozone NAAQS and the EPA approved on May 15, 2009.
See ``RACT for the 8-hour Ozone NAAQS and other Associated SIP
Revisions for the Fine Particulate Matter, Regional Haze, and Transport
of Air Pollution,'' available at https://www.nj.gov/dep/baqp/sip/8-hrRACT-Final.pdf and see 74 FR 22837. The NJDEP, taking a more
stringent approach, believes that significantly higher costs are
warranted and should be considered reasonable with respect to available
technology than were discussed in the Phase 2 Rule. Although no dollar
amount is suggested, the NJDEP identifies five considerations it plans
to apply to sources when determining RACT:
(1) Past New Jersey costs for retrofitting a given control;
(2) Average RACT cost (dollars per tons reduced) for a control
technology and maximum RACT cost. Once a reasonable number of sources
in a source category achieve a lower emission level, other sources
should do the same;
(3) The seriousness of the Region's ozone air quality exceedance.
For nonattainment areas with higher ozone levels, higher costs for
controls are reasonable;
(4) The seriousness of the need to reduce transported air
pollution. As an OTR state, higher costs for RACT are justified; and
(5) The NJDEP plan for addressing economic feasibility in RACT
rules.
The NJDEP's intent is to specify RACT at the lowest emission limit
that a reasonable number of similar facilities had already successfully
implemented for each source category.
[[Page 10460]]
II. The EPA's Evaluation of New Jersey's Submittals
Continue To Operate Under Existing NOX Control Plan
N.J.A.C. 19.13(a)(3) sets forth requirements for facilities that
wish to continue to operate under existing NOX control plans
that were approved prior to May 1, 2005. The regulation requires such
facilities to submit updated proposed NOX control plans to
NJDEP for review. Gerdau Ameristeel originally submitted an FSEL
NOX control plan for a BRF (old BRF) at the Sayreville
Facility to NJDEP in 1995. In 2004, the facility submitted to NJDEP a
proposed FSEL NOX control plan for a replacement BRF; the
new unit was designed with 64 ultra-low NOX burners. On
March 15, 2005, the NJDEP approved the NOX control plan by
authorizing Gerdau Ameristeel to replace the old BRF with the ultra-low
NOX burners.
On October 4, 2016, the Gerdau Ameristeel submitted an updated
proposed NOX control plan to NJDEP requesting to continue to
operate the March 15, 2005 NOX control plan for the
Sayreville BRF that has 64 ultra-low NOX burners and maximum
allowable NOX emission rate of 58.9 tons per year (TPY). On
March 20, 2018, the NJDEP submitted to the EPA a proposal to allow the
continued use of the control options as outlined in the State approved
Gerdau Ameristeel March 15, 2005 NOX control plan.
The Sayreville BRF has a heat input rating of 172.8 million British
Thermal Units per hour (MMBTU/hr) and is permitted under the facility's
CAA Title V operating permit (i.e., PI 18052, BOP 150001) for no more
than 0.1 MMBTU/hr of NOX as a major source with FSEL not to
exceed 17.3 pounds NOX per hour and 58.9 tons NOX
per year. The Sayreville Facility is required to conduct annual
emission testing to demonstrate compliance with 0.1 lb/MMBtu
NOX emission rate limit. The EPA has determined that the
Sayreville BRF identified in the SIP revision are consistent with New
Jersey's NOX RACT regulation and the EPA's guidance.
RACT Analysis
The RACT analysis conducted by Gerdau Ameristeel found eight
control technologies suitable for a typical BRF: (1) Ultra-low
NOX burners currently in use at the facility, (2) low excess
air currently in use at the facility, (3) selective catalytic reduction
(SCR), (4) Low NOX burners, (5) Flue gas recirculation or
reduction of air preheat temperature, (6) Burners out of service, (7)
Selective non-catalytic reduction, and (8) Non-selective catalytic
reduction. Under the regulations, the first three are technologically
feasible, but the latter four were not.
Although the SCR was determined to be technologically feasible, the
Sayreville Facility has major concerns with its implementation. First,
the facility would need to install an evaporative cooler to control the
temperature of the exiting flu gas for this technology to be effective.
Second, the SCR catalyst could become damaged by the BRF process. The
exhaust gas from the BRF contains concentrations of particulate matter,
including metals, which would cause catalyst plugging and masking. The
potential for damage cannot be determined with certainty because the
Sayreville Facility does not currently have SCR units installed on any
BRF that control NOX to compare potential catalyst
poisoning. Moreover, to the best of our knowledge no BRFs in the United
States currently employs SCR units.\3\
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\3\ The EPA's RACT/BACT/LEAR Clearinghouse (RBLC), https://cfpub.epa.gov/rblc/index.cfm?action=Home.Home&lang=en, demonstrates
that 9 U.S. facilities operate a reheat furnace, including billet
reheat furnace, and have NOX emissions. All 9 facilities
have pollution prevention add-on control technologies ultra-low or
low NOX burners and none are equipped with SCR.
---------------------------------------------------------------------------
Cost analysis was conducted for those control technologies found to
be technologically feasible. Since the ultra-low NOX burners
and the low excess air control technologies are currently in use on the
facility's BRF, Gerdau Ameristeel conducted the cost effectiveness
study only for the SCR. The facility concludes that to purchase and
install the SCR will cost $4,279,380 and the annual operating cost
would be $1,164,379 based on a 20-year useful life of the BRF. The cost
effectiveness is based on the annual cost of operating SCR and the
amount of NOX that would be removed. The amount
NOX that would be removed from the SCR is based on 90% (0.9)
control efficiency not to exceed the CAA Title V operating permit limit
of 58.9 NOX TPY (58.9 TPY x 0.9 = 53 TPY). Therefore, the
SCR would result in 53 TPY NOX removed making the cost
effectiveness to be $21,965 per ton NOX removed ($1,164,379
/ 53 = $21,965), which is above the federal RACT guidance. Under EPA
guidance, states should consider in their RACT determinations
technologies that achieve 30-50 percent reduction within a cost range
of $160-$1,300 per ton of NOX removed. See 70 FR 71652.
The SCR control technology was found not to be RACT due to
technological and economical infeasibility under federal and state RACT
criteria.
III. Proposed Action
Gerdau Ameristeel reached agreement with the NJDEP to continue to
operate under the approved March 15, 2005 NOX control plan
that allowed the Sayreville BRF to operate using 64 ultra-low
NOX burners. The Sayreville Facility underwent a change in
ownership to the Commercial Metals Company without changing its
production process or associated equipment. Moreover, the Sayreville
Facility met the regulatory requirements under N.J.A.C. 19.13(a)(3) to
submit and obtain NJDEP approval for an updated proposed NOX
control plan requesting to continue to operate under their 2005
NOX control plan approved prior to May 1, 2005. The updated
NOX control plan demonstrates that the only technically
feasible control technology currently not in use on the Sayreville BRF
is the SCR option and concludes that it is not RACT. Therefore, the EPA
proposes to approve the NJDEP SIP revisions for 8-hour ozone for
Commercial Metals Company continuing to operate under the 2005
NOX Control Plan.
IV. Incorporation by Reference
In this document, we are proposing to include regulatory text in an
EPA final rule that includes incorporation by reference. In accordance
with requirements of 1 CFR 51.5, we are proposing to incorporate by
reference the provisions described above in Section III. Proposed
Action.
The EPA has made, and will continue to make, these documents
generally available electronically through https://www.regulations.gov
and in hard copy at the appropriate EPA office, 290 Broadway, 25th
floor, New York, New York, 10007-1866 (see the ADDRESSES section of
this preamble for more information).
V. Statutory and Executive Order Reviews
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely proposes to approve state law as meeting Federal
requirements and does not impose additional requirements beyond those
imposed by state law. For that reason, this proposed action:
Is not a ``significant regulatory action'' subject to
review by the Office
[[Page 10461]]
of Management and Budget under Executive Order 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 (Public Law 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 does not have tribal implications
as specified by Executive Order 13175, 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. Thus, Executive Order 13175 does not apply to this
action.
List of Subjects 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Nitrogen Dioxide, Intergovernmental Relations, Ozone,
Reporting and recordkeeping requirements.
Authority: 42 U.S.C. 7401 et seq.
Dated: March 9, 2019.
Peter D. Lopez,
Regional Administrator, Region 2.
[FR Doc. 2019-04781 Filed 3-20-19; 8:45 am]
BILLING CODE 6560-50-P