Promulgation of Air Quality Implementation Plans; Arizona; Regional Haze Federal Implementation Plan; Reconsideration, 1608-1615 [2015-00328]
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Federal Register / Vol. 80, No. 8 / Tuesday, January 13, 2015 / Proposed Rules
Permittee, each Customer, any part 440
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to be responsible, for any Property Damage
they sustain and for any Bodily Injury or
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Permittee
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R09–OAR–2014–0861, FRL–9921–49–
Region 9]
Promulgation of Air Quality
Implementation Plans; Arizona;
Regional Haze Federal Implementation
Plan; Reconsideration
AGENCY:
Environmental Protection
Agency.
ACTION:
Proposed rule.
The Environmental Protection
Agency (EPA) is proposing to revise
provisions of the Arizona Regional Haze
(RH) Federal Implementation Plan (FIP)
applicable to the Nelson Lime Plant. In
response to a request for reconsideration
from the plant’s owner, Lhoist North
America of Arizona, Inc. (LNA), we
propose to replace the control
technology demonstration requirements
for nitrogen oxides (NOX) applicable to
Kilns 1 and 2 at the Nelson Lime Plant
with a series of revised recordkeeping
and reporting requirements. Lastly, we
are proposing a correction in the
regulatory language of the final rule
where a table listing the pollution
emission limits for NOX and sulfur
dioxide (SO2) at each kiln was
misprinted. We are seeking comment on
each of these proposed actions.
SUMMARY:
Written comments must be
submitted on or before February 27,
2015. Requests for a public hearing must
be received on or before January 28,
2015.
DATES:
ADDRESSES: See the SUPPLEMENTARY
INFORMATION section for further
instructions on where and how to learn
By: lllllllllllllllllll more about this proposal, request a
Its: lllllllllllllllllll
public hearing, or submit comments.
Customer 1
FOR FURTHER INFORMATION CONTACT:
By: lllllllllllllllllll Thomas Webb, U.S. EPA, Region 9,
Its: lllllllllllllllllll
Planning Office, Air Division, Air-2, 75
Hawthorne Street, San Francisco, CA
94105. Thomas Webb can be reached at
Federal Aviation Administration of the
telephone number (415) 947–4139 and
Department of Transportation on Behalf of
via electronic mail at webb.thomas@
the United States Government
By: lllllllllllllllllll epa.gov.
Its: lllllllllllllllllll SUPPLEMENTARY INFORMATION:
Issued under authority provided by 49.
Throughout this document, ‘‘we,’’ ‘‘us,’’
U.S.C. 106(f) and 44701(a) in Washington,
and ‘‘our’’ refer to EPA.
[Signature lines for each additional customer]
DC, on January 2, 2015.
Shana Dale,
Deputy Associate Administrator, Commercial
Space Transportation.
[FR Doc. 2015–00252 Filed 1–12–15; 8:45 am]
BILLING CODE 4910–13–P
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Table of Contents
I. General Information
II. Background
III. FIP Revision for Nelson Lime Plant
IV. EPA’s Proposed Action
V. Statutory and Executive Order Reviews
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I. General Information
A. Definitions
For the purpose of this document, we
are giving meaning to certain words or
initials as follows:
• The words or initials Act or CAA
mean or refer to the Clean Air Act,
unless the context indicates otherwise.
• The initials ADEQ mean or refer to
the Arizona Department of
Environmental Quality.
• The words Arizona and State mean
the State of Arizona.
• The initials BART mean or refer to
Best Available Retrofit Technology.
• The initials CAA mean or refer to
the Clean Air Act.
• The term Class I area refers to a
mandatory Class I Federal area.1
• The initials CBI mean or refer to
Confidential Business Information.
• The initials CEMS mean or refer to
continuous emission monitoring system
or systems.
• The words EPA, we, us or our mean
or refer to the United States
Environmental Protection Agency.
• The initials FIP mean or refer to
Federal Implementation Plan.
• The initials LNA mean or refer to
LNA North America of Arizona, Inc.
• The initials MMBtu mean or refer to
million British thermal units.
• The initials NOX mean or refer to
nitrogen oxides.
• The initials RH mean or refer to
regional haze.
• The initials RHR mean or refer to
EPA’s Regional Haze Rule.
• The initials SIP mean or refer to
State Implementation Plan.
• The initials SNCR mean or refer to
selective non-catalytic reduction.
• The initials SO2 mean or refer to
sulfur dioxide.
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B. Docket
The proposed action relies on
documents, information, and data that
are listed in the index on https://
www.regulations.gov under docket
number EPA–R09–OAR–2014–0861.
Although listed in the index, some
information is not publicly available
(e.g., Confidential Business Information
(CBI)). Certain other material, such as
copyrighted material, is publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically at https://
www.regulations.gov or in hard copy at
the Planning Office of the Air Division,
1 Although states and tribes may designate as
Class I additional areas which they consider to have
visibility as an important value, the requirements of
the visibility program set forth in section 169A of
the CAA apply only to ‘‘mandatory Class I Federal
areas.’’
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AIR–2, EPA Region 9, 75 Hawthorne
Street, San Francisco, CA 94105. EPA
requests that you contact the individual
listed in the FOR FURTHER INFORMATION
CONTACT section to view the hard copy
of the docket. You may view the hard
copy of the docket Monday through
Friday, 9–5:00 PDT, excluding Federal
holidays.
C. Instructions for Submitting
Comments to EPA
Written comments must be submitted
on or before February 27, 2015. Submit
your comments, identified by Docket ID
No. EPA–R09–OAR–2014–0861, by one
of the following methods:
• Federal Rulemaking portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Email: webb.thomas@epa.gov.
• Fax: 415–947–3579 (Attention:
Thomas Webb).
• Mail, Hand Delivery or Courier:
Thomas Webb, EPA Region 9, Air
Division (AIR–2), 75 Hawthorne Street,
San Francisco, California 94105. Hand
and courier deliveries are only accepted
Monday through Friday, 8:30 a.m.–4:30
p.m., excluding Federal holidays.
Special arrangements should be made
for deliveries of boxed information.
EPA’s policy is to include all
comments received in the public docket
without change. We may make
comments available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be CBI or other information
for which disclosure is restricted by
statute. Do not submit information that
you consider to be CBI or that is
otherwise protected through https://
www.regulations.gov or email. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an email comment directly
to EPA, without going through https://
www.regulations.gov, we will include
your email address as part of the
comment that is placed in the public
docket and made available on the
Internet. If you submit an electronic
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should not
include special characters or any form
of encryption, and be free of any defects
or viruses.
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D. Submitting Confidential Business
Information
Do not submit CBI to EPA through
https://www.regulations.gov or by email.
Clearly mark the part or all of the
information that you claim as CBI. For
CBI information in a disk or CD–ROM
that you mail to EPA, mark the outside
of the disk or CD–ROM as CBI and
identify electronically within the disk or
CD–ROM the specific information that
is claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI,
you must submit a copy of the comment
that does not contain the information
claimed as CBI for inclusion in the
public docket. We will not disclose
information so marked except in
accordance with procedures set forth in
40 CFR part 2.
E. Tips for Preparing Your Comments
When submitting comments,
remember to:
• Identify the rulemaking by docket
number and other identifying
information (e.g., subject heading,
Federal Register date, and page
number).
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline.
F. Public Hearings
If anyone contacts EPA by January 28,
2015 requesting to speak at a public
hearing, EPA will schedule a public
hearing and announce the hearing in the
Federal Register. Contact Thomas Webb
at (415) 947–4139 or at webb.thomas@
epa.gov to request a hearing or to
determine if a hearing will be held.
II. Background
A. Summary of Statutory and
Regulatory Requirements
Congress created a program for
protecting visibility in the nation’s
national parks and wilderness areas in
section 169A of the 1977 Amendments
to the CAA. This section of the CAA
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establishes as a national goal the
‘‘prevention of any future, and the
remedying of any existing, impairment
of visibility in mandatory Class I
Federal areas which impairment results
from man-made air pollution.’’ 2 It also
directs states to evaluate the use of
retrofit controls at certain larger, often
uncontrolled, older stationary sources in
order to address visibility impacts from
these sources. Specifically, section
169A(b)(2)(A) of the CAA requires states
to revise their State Implementation
Plans (SIPs) to contain such measures as
may be necessary to make reasonable
progress towards the natural visibility
goal, including a requirement that
certain categories of existing major
stationary sources built between 1962
and 1977 procure, install, and operate
best available retrofit technology
(BART) controls. These sources are
referred to as ‘‘BART-eligible’’ sources.3
In the 1990 CAA Amendments,
Congress amended the visibility
provisions in the CAA to focus attention
on the problem of regional haze, which
is visibility impairment produced by a
multitude of sources and activities
located across a broad geographic area.4
We promulgated the Regional Haze Rule
(RHR) in 1999, which requires states to
develop and implement SIPs to ensure
reasonable progress toward improving
visibility in mandatory Class I Federal
areas 5 by reducing emissions that cause
or contribute to regional haze.6 Under
the Regional Haze Rule (RHR), states are
directed to conduct BART
determinations for BART-eligible
sources that may be anticipated to cause
or contribute to any visibility
impairment in a Class I area.7
B. History of FIP BART Determination
The Arizona Department of
Environmental Quality (ADEQ)
submitted a Regional Haze SIP to EPA
on February 28, 2011. EPA promulgated
two final rules approving in part and
disapproving in part the Arizona RH
SIP. The first final rule addressed the
State’s BART determinations for three
power plants (Apache, Cholla, and
Coronado).8 The second final rule,
which addressed the remaining
42 U.S.C. 7491(a)(1).
40 CFR 51.301.
4 See CAA section 169B, 42 U.S.C. 7492.
5 Areas designated as mandatory Class I Federal
areas consist of national parks exceeding 6000
acres, wilderness areas, and national memorial
parks exceeding 5000 acres, and all international
parks that were in existence on August 7, 1977. 42
U.S.C. 7472(a). When we use the term ‘‘Class I area’’
in this action, we mean a ‘‘mandatory Class I
Federal area.’’
6 See generally 40 CFR 51.308.
7 40 CFR 51.308(e).
8 77 FR 72512 (December 5, 2012).
2
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elements of the Arizona RH SIP,
included our disapproval of the State’s
determination that the Nelson Lime
Plant was not subject to BART.9
In a third final rule, EPA found that
the Nelson Lime Plant was subject to
BART and made a BART determination
for the plant, as part of the Arizona RH
FIP.10 EPA set BART emission limits for
NOX at the Nelson Lime Plant of 3.80 lb/
ton of limestone product for Kiln 1 and
2.61 lb/ton of limestone product for Kiln
2 based on a 12-month rolling average;
and a combined limit for Kilns 1 and 2
of 3.27 tons of NOX/day on a 30-day
rolling average. These limits are
consistent with the use of SNCR control
technology and represent a 50 percent
reduction from baseline emission rates.
The FIP also included monitoring,
recordkeeping, and reporting
requirements, and established a
compliance deadline for the final NOX
emission limits of September 3, 2017,
which is three years from the
publication date of the final rule.
Finally, we received certain comments
alleging that an SNCR control efficiency
of 50 percent was unsupported, and that
SNCR was capable of achieving control
efficiency as high as 80 percent. In
responses to these comments in our
final rule, we noted that the commenters
were unable to provide information
indicating that an SNCR control
efficiency better than 50 percent was
achievable at a lime kiln. As a result,
our final rule established NOX emission
limits consistent with an SNCR control
efficiency of 50 percent. However, in
response to these comments, as well as
the lack of data regarding the
performance of SNCR on lime kilns, the
final rule included a series of control
technology demonstration requirements
for Kiln 1 and Kiln 2 to ensure the
optimization of the SNCR systems
installed at the Nelson Lime Plant.
C. Petition for Reconsideration and Stay
LNA submitted a petition to EPA on
October 31, 2014, seeking
administrative reconsideration and a
partial stay of the final rule under CAA
section 307(d)(7)(B).11 Specifically, LNA
requested that EPA eliminate the control
technology demonstration requirements
for the Nelson Lime Plant. In an
attachment to the petition, LNA
provided additional data regarding
SNCR performance at lime kilns located
at another LNA facility, the O’Neal Lime
Plant in Calera, Alabama. In the
petition, LNA also requested a stay if
78 FR 46142 (July 30, 2013).
79 FR 52420 (September 3, 2014).
11 Letter from Eric Hiser, Jorden Bischoff & Hiser,
to Regina McCarthy, EPA (October 31, 2014).
9
EPA did not take action prior to
December 31, 2014. LNA requested a
stay on the grounds that the control
technology demonstration requirements
would not provide sufficient time to
meet the SO2 and NOX BART emission
limits. LNA asserted that the time
needed to implement the demonstration
requirements, in particular the
requirement to collect six months of
uncontrolled NOX emission data, would
delay the critical path schedule for
SNCR installation beyond the
compliance date. EPA sent a letter to
LNA on November 20, 2014, granting
reconsideration of the optimization
protocol requirements pursuant to CAA
section 307(d)(7)(B).12 Today’s notice of
proposed rulemaking constitutes EPA’s
proposed action on the reconsideration.
III. FIP Revision for Nelson Lime Plant
A. Summary of FIP Revision
This proposed rule consists of several
components: removal of the control
technology demonstration requirements,
revised recordkeeping and reporting
requirements, and an error correction to
a table in our September 3, 2014, final
rule. This proposed rule does not
change any of the emission limits,
compliance deadlines, or the
compliance determination methods
established in the final rule.
B. EPA’s Evaluation of Eliminating
Control Technology Demonstration
Requirements
EPA is proposing to remove the
control technology demonstration
requirements from the final rule based
on information provided in LNA’s
petition for reconsideration. In
particular, in a letter dated October 2,
2014, and enclosed with the petition,
LNA provided new data concerning
operation of SNCR at another of its
facilities, the O’Neal Lime Plant. The
O’Neal Lime Plant originally consisted
of Kiln 1, but was later expanded
through the construction of Kiln 2. In
order for the construction of Kiln 2 not
to trigger major new source review for
NOX emissions, LNA elected to install
SNCR on both Kilns 1 and 2 to maintain
NOX emissions below thresholds for
major new source review. LNA provided
information comparing the physical
design of the two kilns at the O’Neal
Lime Plant with the two kilns at the
Nelson Lime Plant. LNA indicated that
although the two O’Neal kilns are not
identical to the Nelson kilns, O’Neal
Kiln 1 is more similar in design to the
Nelson kilns than O’Neal Kiln 2. We
consider this comparison reasonable. Of
10
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12 Letter from Jared Blumenfeld, EPA to Eric
Hiser, Jorden Bischoff & Hiser (November 20, 2014).
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Federal Register / Vol. 80, No. 8 / Tuesday, January 13, 2015 / Proposed Rules
the two O’Neal kilns, Kiln 1 is closer in
age, physical dimensions, lime
production rate, and fuel efficiency to
the Nelson kilns than Kiln 2.
The remainder of the October 2, 2014,
letter summarizes NOX emission data
from specific days of operation at
O’Neal Kiln 1 to evaluate the SNCR
control efficiency of the kiln. Evaluating
the control efficiency involves
comparing uncontrolled emission rates
with controlled emission rates from Kiln
1. However, uncontrolled NOX emission
data for the O’Neal plant are limited,
because the facility did not operate with
a continuous emission monitoring
system (CEMS) for NOX prior to
installing SNCR.13 As a result,
uncontrolled NOX emission data are
limited to those periods of time
following SNCR installation during
which the SNCR system did not operate.
LNA provided emission data from six
days during which the SNCR did not
operate to represent uncontrolled NOX
emission rates. NOX emission data from
those periods corresponding to hours of
SNCR operation were also included as
a representation of controlled NOX
emission rates. Based on this analysis,
the SNCR control efficiency of O’Neal
Kiln 1 varied from 42 to 61 percent.
This range of control efficiency
represents SNCR performance over
relatively short-term periods of less than
24 hours. For example, the highest
observed control efficiency (61 percent)
corresponds to a period ending on
December 1, 2011, and consists of a
comparison of six hours of uncontrolled
emissions with eight hours of controlled
emissions. As noted in the final rule in
regard to control efficiencies for dry
sorbent injection, we do not consider
the upper range of short-term control
efficiencies necessarily to be sustainable
over longer periods, such as on an
annual average basis.14 Therefore, while
the emission data provided by LNA
indicate that a 61 percent SNCR control
efficiency was achievable over short
term periods (lasting several hours), we
do not necessarily consider 61 percent
control efficiency to be achievable over
longer averaging periods, such as an
annual average or 30-day average. For
cement kilns, a source category similar
to lime kilns, the highest short-term
emission rates can be as much as 25–50
percent greater than the highest annual
average or 30-day average emission
rates.15 As a result, given the short-term
13 This
is common with older lime and cement
plants, and is similar to the situation at the Nelson
plant, which does not currently operate NOX CEMS.
14 79 FR 52439.
15 For comparison, we have examined the
maximum 24-hr average, 30-day average, and
annual average emissions for Kiln 4 at the Phoenix
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nature of the emission data indicating a
maximum 61 percent SNCR control
efficiency, we consider the use of a 50
percent control efficiency on a longer
annual average basis to be reasonable for
the Nelson kilns.
Accordingly, we propose to find that
the data from the O’Neal kilns are
sufficient to establish that an SNCR
control efficiency of 50 percent is
appropriate for the Nelson kilns for
purposes of BART. While we still
consider it necessary to ensure that the
SNCR system be optimized, we do not
consider it necessary for LNA to adhere
to the relatively detailed and prescribed
procedures contained in the control
technology demonstration requirements.
Therefore, we are proposing to remove
the control technology demonstration
requirements included in the final rule,
and, as described below, are proposing
requirements that will require LNA to
report similar information in a less
prescribed manner.
1611
performed on the SNCR system, a
discussion of whether the adjustment
affected the NOX emission rate, a
description of the range over which the
adjustment was examined, and a
discussion of how the adjustment will
be reflected or accounted for in kiln
operating practices.
D. Error Correction
We are proposing a minor correction
to a table printed in our September 3,
2014, final rule at 79 FR 52480. The
table, which is codified at 40 CFR
52.145(i)(3)(i) and lists NOX and SO2
limits for the Nelson Plant Kilns,
appears with incorrect column labels
due to a misprint in the Federal
Register. The table appears with the
correct labels in the proposed regulatory
text that follows this proposed rule.
E. Non-interference With Applicable
Requirements
The CAA requires that any revision to
C. Revised Recordkeeping and Reporting
an implementation plan shall not be
Requirements
approved by the Administrator if the
We are proposing several additional
revision would interfere with any
reporting and recordkeeping
applicable requirement concerning
requirements, including a summary of
attainment and reasonable further
SNCR design and a summary of SNCR
progress or any other applicable
debugging and process improvement
requirement of the CAA.16 Today’s
activities, to replace the control
proposed revisions would not affect any
technology demonstration requirements
applicable requirements of the CAA
in the FIP for Nelson Lime Plant. As
because they would not alter the
described in III.B above, we consider it
amount or timing of emission
necessary to include provisions for
reductions from the Nelson Lime Plant.
SNCR optimization. Given the NOX
In particular, the proposed replacement
emission data provided by LNA from
of the control technology demonstration
the O’Neal Plant indicating that 50
percent SNCR control efficiency has
requirements with a series of
been achieved at a lime kiln, we do not
recordkeeping and reporting
consider it necessary for optimization
requirements would not alter any of the
measures to be as prescriptive and
applicable emission limitations,
detailed as established in our September compliance determination
4, 2014, final rule. Specifically, we
methodologies, or compliance
propose to require LNA to submit a
deadlines. Therefore, we propose to find
summary of the SNCR design prior to
that these revisions would comply with
commencing construction of the
CAA section 110(l).
ammonia injection system at Kilns 1
IV. EPA’s Proposed Action
and 2, including information regarding
reagent type, locations selected for
For the reasons described above, EPA
reagent injection, reagent injection rate,
proposes to revise the Arizona Regional
equipment arrangement, and kiln
Haze FIP to eliminate the control
characteristics. We also propose to
technology demonstration requirements
require LNA to submit a summary of
at the Nelson Lime Plant and replace
SNCR debugging and process
them with additional recordkeeping and
improvement activities, including a
reporting requirements. This revision
description of each process adjustment
would constitute our action on LNA’s
Cement Plant (see spreadsheet ‘‘Phoenix Cement
Petition for Reconsideration of the FIP.
Kiln 4 NOX Emissions 2005–10 (public).xlsx.’’ The
Phoenix Cement Kiln 4 data illustrate the
substantial variability in emission rates from a
cement kiln when examining emissions on shortterm versus longer-term averaging periods. Given
the similarity between lime kilns and cement kilns,
we expect similar variability in the short-term
versus longer-term emission rates from lime kilns.
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16 CAA
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Section 110(l), 42 U.S.C. 7410(l).
13JAP1
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V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This proposed action is not a
‘‘significant regulatory action’’ under
the terms of Executive Order 12866 (58
FR 51735, October 4, 1993) and is
therefore not subject to review under
Executive Orders 12866 and 13563 (76
FR 3821, January 21, 2011). This
proposed rule applies to only one
facility and is therefore not a rule of
general applicability.
B. Paperwork Reduction Act
This action does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. Burden is
defined at 5 CFR 1320.3(b).
asabaliauskas on DSK5VPTVN1PROD with PROPOSALS
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of today’s proposed rule on small
entities, small entity is defined as: (1) A
small business as defined by the Small
Business Administration’s (SBA)
regulations at 13 CFR 121.201; (2) a
small governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field. Pursuant to 13
CFR 121.201, footnote 1, a firm is small
if it is in NAICS 327410 (lime
manufacturing) and the concern and its
affiliates have no more than 500
employees. LNA is affiliated with the
LNA Group, which has more than 5,500
employees.17 Therefore, LNA is not a
small business.
D. Unfunded Mandates Reform Act
(UMRA)
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), 2 U.S.C.
17 https://www.LNA.com/facts-and-figures-LNAgroup-2013.
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1531–1538, requires Federal agencies,
unless otherwise prohibited by law, to
assess the effects of their regulatory
actions on State, local, and tribal
governments and the private sector.
Federal agencies must also develop a
plan to provide notice to small
governments that might be significantly
or uniquely affected by any regulatory
requirements. The plan must enable
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates and must
inform, educate, and advise small
governments on compliance with the
regulatory requirements.
This proposed rule does not contain
a Federal mandate that may result in
expenditures of $100 million or more
for state, local, and tribal governments,
in the aggregate, or the private sector in
any one year. Thus, this rule is not
subject to the requirements of sections
202 or 205 of UMRA.
This proposed rule is also not subject
to the requirements of section 203 of
UMRA because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. This
proposed rule does not impose
regulatory requirements on any
government entity.
This proposed rule does not have
tribal implications, as specified in
Executive Order 13175. It will not have
substantial direct effects on tribal
governments. Thus, Executive Order
13175 does not apply to this rule. EPA
specifically solicits additional comment
on this proposed rule from tribal
officials.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or in the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicits comment on this
proposed action from State and local
officials.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law 104–
113, 12 (10) (15 U.S.C. 272 note) directs
EPA to use voluntary consensus
standards (VCS) in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impractical. VCS are
technical standards (e.g., materials
specifications, test methods, sampling
procedures, and business practices) that
are developed or adopted by the VCS
bodies. The NTTAA directs EPA to
provide Congress, through annual
reports to OMB, with explanations
when the Agency decides not to use
available and applicable VCS.
EPA believes that VCS are
inapplicable to this action. Today’s
action does not require the public to
perform activities conducive to the use
of VCS.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Under Executive Order 13175 (65 FR
67249, November 9, 2000), EPA may not
issue a regulation that has tribal
implications, that imposes substantial
direct compliance costs, and that is not
required by statute, unless the federal
government provides the funds
necessary to pay the direct compliance
costs incurred by tribal governments, or
EPA consults with tribal officials early
in the process of developing the
proposed regulation and develops a
tribal summary impact statement.
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G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
EPA interprets EO 13045 (62 FR
19885, April 23, 1997) as applying only
to those regulatory actions that concern
health or safety risks, such that the
analysis required under section 5–501 of
the EO has the potential to influence the
regulation. This action is not subject to
EO 13045 because it does not establish
an environmental standard intended to
mitigate health or safety risks. This
proposed action addresses regional haze
and visibility protection.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 (66 FR 28355 (May 22,
2001)), because it is exempt under
Executive Order 12866.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629,
February 16, 1994), establishes federal
executive policy on environmental
justice. Its main provision directs
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federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low- income
populations in the United States.
EPA has determined that this
proposed rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
because it does not change the level of
environmental protection for any
affected populations.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Nitrogen oxides,
Particulate matter, Reporting and
recordkeeping requirements, Sulfur
dioxide, Visibility. Incorporation by
Reference.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 29, 2014.
Jared Blumenfeld,
Regional Administrator, EPA Region IX.
Part 52, chapter I, title 40 of the Code
of Federal Regulations is proposed to be
amended as follows:
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart D—Arizona
2. Amend § 52.145 by:
a. Revising paragraph (i); and
b. Removing Appendix B to
§ 52.145—Lime Kiln Control
Technology Demonstration
Requirements.
The revision reads as follows:
■
■
■
§ 52.145
POLLUTANT EMISSION LIMIT
Kiln ID
Visibility protection.
*
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Ammonia injection shall include any
of the following: Anhydrous ammonia,
aqueous ammonia, or urea injection.
Continuous emission monitoring
system or CEMS means the equipment
required by this section to sample,
analyze, measure, and provide, by
means of readings recorded at least once
every 15 minutes (using an automated
data acquisition and handling system
(DAHS)), a permanent record of NOX
emissions, SO2 emissions, diluent, and
stack gas volumetric flow rate.
Kiln means either of the kilns
identified in paragraph (i)(1) of this
section.
Kiln 1 means lime kiln 1, as identified
in paragraph (i)(1) of this section.
Kiln 2 means lime kiln 2, as identified
in paragraph (i)(1) of this section.
Kiln operating day means a 24-hour
period between 12 midnight and the
following midnight during which there
is operation of Kiln 1, Kiln 2, or both
kilns at any time.
Kiln operation means any period
when any raw materials are fed into the
Kiln or any period when any
combustion is occurring or fuel is being
fired in the Kiln.
Lime product means the product of
the lime-kiln calcination process,
including calcitic lime, dolomitic lime,
and dead-burned dolomite.
NOX means oxides of nitrogen.
Owner/operator means any person
who owns or who operates, controls, or
supervises a kiln identified in paragraph
(i)(1) of this section.
SO2 means sulfur dioxide.
(3) Emission limitations. (i) The
owner/operator of the kilns identified in
paragraph (i)(1) of this section shall not
emit or cause to be emitted pollutants in
excess of the following limitations in
pounds of pollutant per ton of lime
product (lb/ton), from any kiln. Each
emission limit shall be based on a 12month rolling basis.
*
*
*
*
(i) Source-specific federal
implementation plan for regional haze
at Nelson Lime Plant—
(1) Applicability. This paragraph (i)
applies to the owner/operator of the
lime kilns designated as Kiln 1 and Kiln
2 at the Nelson Lime Plant located in
Yavapai County, Arizona.
(2) Definitions. Terms not defined in
this paragraph (i)(2) shall have the
meaning given them in the Clean Air
Act or EPA’s regulations implementing
the Clean Air Act. For purposes of this
paragraph (i):
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NOX
Kiln 1 .........................
Kiln 2 .........................
3.80
2.61
SO2
9.32
9.73
(ii) The owner/operator of the kilns
identified in paragraph (i)(1) of this
section shall not emit or cause to be
emitted pollutants in excess of 3.27 tons
of NOX per day and 10.10 tons of SO2
per day, combined from both kilns,
based on a rolling 30-kiln-operating-day
basis.
(4) Compliance dates. (i) The owner/
operator of each kiln shall comply with
the NOX emission limitations and other
NOX-related requirements of this
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1613
paragraph (i) no later than September 4,
2017.
(ii) The owner/operator of each kiln
shall comply with the SO2 emission
limitations and other SO2-related
requirements of this paragraph (i) no
later than March 3, 2016.
(5) [Reserved]
(6) Compliance determination—(i)
Continuous emission monitoring
system. At all times after the compliance
dates specified in paragraph (i)(4) of this
section, the owner/operator of kilns 1
and 2 shall maintain, calibrate, and
operate a CEMS, in full compliance with
the requirements found at 40 CFR 60.13
and 40 CFR part 60, appendices B and
F, to accurately measure diluent, stack
gas volumetric flow rate, and
concentration by volume of NOX and
SO2 emissions into the atmosphere from
kilns 1 and 2. The CEMS shall be used
by the owner/operator to determine
compliance with the emission
limitations in paragraph (i)(3) of this
section, in combination with data on
actual lime production. The owner/
operator must operate the monitoring
system and collect data at all required
intervals at all times that an affected
kiln is operating, except for periods of
monitoring system malfunctions, repairs
associated with monitoring system
malfunctions, and required monitoring
system quality assurance or quality
control activities (including, as
applicable, calibration checks and
required zero and span adjustments).
(ii) Ammonia consumption
monitoring. Upon and after the
completion of installation of ammonia
injection on a kiln, the owner or
operator shall install, and thereafter
maintain and operate, instrumentation
to continuously monitor and record
levels of ammonia consumption for that
kiln.
(iii) Compliance determination for lb
per ton NOX limit. Compliance with the
NOX emission limits described in
paragraph (i)(3)(i) of this section shall be
determined based on a rolling 12-month
basis. The 12-month rolling NOX
emission rate for each kiln shall be
calculated within 30 days following the
end of each calendar month in
accordance with the following
procedure: Step one, sum the hourly
pounds of NOX emitted for the month
just completed and the eleven (11)
months preceding the month just
completed to calculate the total pounds
of NOX emitted over the most recent
twelve (12) month period for that kiln;
Step two, sum the total lime product, in
tons, produced during the month just
completed and the eleven (11) months
preceding the month just completed to
calculate the total lime product
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produced over the most recent twelve
(12) month period for that kiln; Step
three, divide the total amount of NOX
calculated from Step one by the total
lime product calculated from Step two
to calculate the 12-month rolling NOX
emission rate for that kiln. Each 12month rolling NOX emission rate shall
include all emissions and all lime
product that occur during all periods
within the 12-month period, including
emissions from startup, shutdown, and
malfunction.
(iv) Compliance determination for lb
per ton SO2 limit. Compliance with the
SO2 emission limits described in
paragraph (i)(3)(i) of this section shall be
determined based on a rolling 12month basis. The 12-month rolling SO2
emission rate for each kiln shall be
calculated within 30 days following the
end of each calendar month in
accordance with the following
procedure: Step one, sum the hourly
pounds of SO2 emitted for the month
just completed and the eleven (11)
months preceding the month just
completed to calculate the total pounds
of SO2 emitted over the most recent
twelve (12) month period for that kiln;
Step two, sum the total lime product, in
tons, produced during the month just
completed and the eleven (11) months
preceding the month just completed to
calculate the total lime product
produced over the most recent twelve
(12) month period for that kiln; Step
three, divide the total amount of SO2
calculated from Step one by the total
lime product calculated from Step two
to calculate the 12-month rolling SO2
emission rate for that kiln. Each 12month rolling SO2 emission rate shall
include all emissions and all lime
product that occur during all periods
within the 12-month period, including
emissions from startup, shutdown, and
malfunction.
(v) Compliance determination for ton
per day NOX limit. Compliance with the
NOX emission limit described in
paragraph (i)(3)(ii) of this section shall
be determined based on a rolling 30kiln-operating-day basis. The rolling 30kiln operating day NOX emission rate
for the kilns shall be calculated for each
kiln operating day in accordance with
the following procedure: Step one, sum
the hourly pounds of NOX emitted from
both kilns for the current kiln operating
day and the preceding twenty-nine (29)
kiln-operating-day period for both kilns;
Step two, divide the total pounds of
NOX calculated from Step one by two
thousand (2,000) to calculate the total
tons of NOX; Step three, divide the total
tons of NOX calculated from Step two by
thirty (30) to calculate the rolling 30kiln operating day NOX emission rate
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Jkt 235001
for both kilns. Each rolling 30-kiln
operating day NOX emission rate shall
include all emissions that occur from
both kilns during all periods within any
kiln operating day, including emissions
from startup, shutdown, and
malfunction.
(vi) Compliance determination for ton
per day SO2 limit. Compliance with the
SO2 emission limit described in
paragraph (i)(3)(ii) of this section shall
be determined based on a rolling 30kiln-operating-day basis. The rolling 30kiln operating day SO2 emission rate for
the kilns shall be calculated for each
kiln operating day in accordance with
the following procedure: Step one, sum
the hourly pounds of SO2 emitted from
both kilns for the current kiln operating
day and the preceding twenty-nine (29)
kiln operating days, to calculate the
total pounds of SO2 emitted over the
most recent thirty (30) kiln operating
day period for both kilns; Step two,
divide the total pounds of SO2
calculated from Step one by two
thousand (2,000) to calculate the total
tons of SO2; Step three, divide the total
tons of SO2 calculated from Step two by
thirty (30) to calculate the rolling 30kiln operating day SO2 emission rate for
both kilns. Each rolling 30-kiln
operating day SO2 emission rate shall
include all emissions that occur from
both kilns during all periods within any
kiln operating day, including emissions
from startup, shutdown, and
malfunction.
(7) Recordkeeping. The owner/
operator shall maintain the following
records for at least five years:
(i) All CEMS data, including the date,
place, and time of sampling or
measurement; parameters sampled or
measured; and results.
(ii) All records of lime production.
(iii) Monthly rolling 12-month
emission rates of NOX and SO2,
calculated in accordance with
paragraphs (i)(6)(iii) and (iv) of this
section.
(iv) Daily rolling 30-kiln operating
day emission rates of NOX and SO2
calculated in accordance with
paragraphs (i)(6)(v) and (vi) of this
section.
(v) Records of quality assurance and
quality control activities for emissions
measuring systems including, but not
limited to, any records specified by 40
CFR part 60, appendix F, Procedure 1,
as well as the following:
(A) The occurrence and duration of
any startup, shutdown, or malfunction,
performance testing, evaluations,
calibrations, checks, adjustments
maintenance, duration of any periods
during which a CEMS or COMS is
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inoperative, and corresponding
emission measurements.
(B) Date, place, and time of
measurement or monitoring equipment
maintenance activity;
(C) Operating conditions at the time of
measurement or monitoring equipment
maintenance activity;
(D) Date, place, name of company or
entity that performed the measurement
or monitoring equipment maintenance
activity and the methods used; and
(E) Results of the measurement or
monitoring equipment maintenance.
(vi) Records of ammonia
consumption, as recorded by the
instrumentation required in paragraph
(i)(6)(ii) of this section.
(vii) Records of all major maintenance
activities conducted on emission units,
air pollution control equipment, CEMS,
and lime production measurement
devices.
(viii) All other records specified by 40
CFR part 60, appendix F, Procedure 1.
(8) Reporting. All reports required
under this section shall be submitted by
the owner/operator to the Director,
Enforcement Division, U.S.
Environmental Protection Agency,
Region 9, electronically via email to
aeo_r9@epa.gov. Any data that are
required under this section shall be
submitted in Excel format. Reports
required under paragraphs (i)(8)(iii)
through (i)(8)(v) of this section shall be
submitted within 30 days after the
applicable compliance date(s) in
paragraph (i)(4) of this section and at
least semiannually thereafter, within 30
days after the end of a semiannual
period. The owner/operator may submit
reports more frequently than
semiannually for the purposes of
synchronizing reports required under
this section with other reporting
requirements, such as the title V
monitoring report required by 40 CFR
70.6(a)(3)(iii)(A), but at no point shall
the duration of a semiannual period
exceed six months.
(i) Prior to commencing construction
of the ammonia injection system, the
owner/operator shall submit to EPA a
summary report of the design of the
SNCR system. Elements of this summary
report shall include: Reagent type,
description of the locations selected for
reagent injection, reagent injection rate
(expressed as a molar ratio of reagent to
NOX), equipment list, equipment
arrangement, and a summary of kiln
characteristics that were relied upon as
the design basis for the SNCR system.
(ii) By October 3, 2017, the owner/
operator shall submit to EPA a summary
of any process improvement or
debugging activities that were
performed on the SNCR system.
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Elements of this summary report shall
include: A description of each process
adjustment performed on the SNCR
system, a discussion of whether the
adjustment affected NOX emission rate
(including CEMS data that may have
been recorded while the adjustment was
in progress), a description of the range
(if applicable) over which the
adjustment was examined, and a
discussion of how the adjustment will
be reflected or accounted for in kiln
operating practices. In addition, to the
extent that the owner/operator evaluates
the impact of varying reagent injection
rate on NOX emissions, the owner/
operator shall include the following
information: The range of reagent
injection rates evaluated (expressed as a
molar ratio of reagent to average NOX
concentration), reagent injection rate,
average NOX concentration, lime
production rate, kiln flue gas
temperature, and the presence of any
detached plumes from the kiln exhaust.
(iii) The owner/operator shall submit
a report that lists the daily rolling 30kiln operating day emission rates for
NOX and SO2, calculated in accordance
with paragraphs (i)(6)(iii) and (iv) of this
section.
(iv) The owner/operator shall submit
a report that lists the monthly rolling
12-month emission rates for NOX and
SO2, calculated in accordance with
paragraphs (i)(6)(v) and (vi) of this
section.
(v) The owner/operator shall submit
excess emissions reports for NOX and
SO2 limits. Excess emissions means
emissions that exceed any of the
emissions limits specified in paragraph
(i)(3) of this section. The reports shall
include the magnitude, date(s), and
duration of each period of
excessemissions; specific identification
of each period of excess emissions that
occurs during startups, shutdowns, and
malfunctions of the kiln; the nature and
cause of any malfunction (if known);
and the corrective action taken or
preventative measures adopted.
(vi) The owner/operator shall submit
a summary of CEMS operation, to
include dates and duration of each
period during which the CEMS was
inoperative (except for zero and span
adjustments and calibration checks),
reason(s) why the CEMS was
inoperative and steps taken to prevent
recurrence, and any CEMS repairs or
adjustments.
(vii) The owner/operator shall submit
results of all CEMS performance tests
required by 40 CFR part 60, Appendix
F, Procedure 1 (Relative Accuracy Test
Audits, Relative Accuracy Audits, and
Cylinder Gas Audits).
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Jkt 235001
(viiii) When no excess emissions have
occurred or the CEMS has not been
inoperative, repaired, or adjusted during
the reporting period, the owner/operator
shall state such information in the
semiannual report.
(9) Notifications. All notifications
required under this section shall be
submitted by the owner/operator to the
Director, Enforcement Division (Mail
Code ENF–2–1), U.S. Environmental
Protection Agency, Region 9, 75
Hawthorne Street, San Francisco,
California 94105–3901.
(i) The owner/operator shall submit
notification of commencement of
construction of any equipment which is
being constructed to comply with the
NOX emission limits in paragraph (i)(3)
of this section.
(ii) The owner/operator shall submit
semiannual progress reports on
construction of any such equipment.
(iii) The owner/operator shall submit
notification of initial startup of any such
equipment.
(10) Equipment operations. (i) At all
times, including periods of startup,
shutdown, and malfunction, the owner/
operator shall, to the extent practicable,
maintain and operate the kilns,
including associated air pollution
control equipment, in a manner
consistent with good air pollution
control practices for minimizing
emissions. Pollution control equipment
shall be designed and capable of
operating properly to minimize
emissions during all expected operating
conditions. Determination of whether
acceptable operating and maintenance
procedures are being used will be based
on information available to the Regional
Administrator, which may include, but
is not limited to, monitoring results,
review of operating and maintenance
procedures, and inspection of the kilns.
(ii) After completion of installation of
ammonia injection on a kiln, the owner/
operator shall inject sufficient ammonia
to achieve compliance with the NOX
emission limits from paragraph (i)(3) of
this section for that kiln while
preventing excessive ammonia
emissions.
(11) Enforcement. Notwithstanding
any other provision in this
implementation plan, any credible
evidence or information relevant as to
whether the kiln would have been in
compliance with applicable
requirements if the appropriate
performance or compliance test had
been performed can be used to establish
whether or not the owner/operator has
violated or is in violation of any
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1615
standard or applicable emission limit in
the plan.
[FR Doc. 2015–00328 Filed 1–12–15; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL COMMUNICATIONS
COMMISSION
47 CFR Part 73
[MB Docket No. 14–257; RM–11743; DA 14–
1868]
Radio Broadcasting Services; Wright
City, Oklahoma
Federal Communications
Commission.
ACTION: Proposed rule.
AGENCY:
This document requests
comments on a Petition for Rule Making
filed by Charles Crawford, proposing to
amend the FM Table of Allotments,
Section 73.202(b) of the Commission’s
Rules, by allotting Channel 295A at
Wright City, Oklahoma, as the
community’s first local service. A staff
engineering analysis indicates that
Channel 295A can be allotted to Wright
City consistent with the minimum
distance separation requirements of the
Commission’s Rules with a site
restriction located 14 kilometers (8.6
miles) east of the community. The
reference coordinates are 34–04–44 NL
and 94–51–15 WL.
DATES: Comments must be filed on or
before February 9, 2015, and reply
comments on or before February 24,
2015.
ADDRESSES: Secretary, Federal
Communications Commission, 445 12th
Street SW., Washington, DC 20554. In
addition to filing comments with the
FCC, interested parties should serve the
petitioner as follows: Charles Crawford,
2215 Cedar Springs Rd., #1605, Dallas,
Texas 75201.
FOR FURTHER INFORMATION CONTACT:
Rolanda F. Smith, Media Bureau, (202)
418–2700.
SUPPLEMENTARY INFORMATION: This is a
synopsis of the Commission’s Notice of
Proposed Rule Making, MB Docket No.
14–257, adopted December 18, 2014,
and released December 19, 2014. The
full text of this Commission decision is
available for inspection and copying
during normal business hours in the
FCC’s Reference Information Center at
Portals II, CY–A257, 445 12th Street
SW., Washington, DC 20554. This
document may also be purchased from
the Commission’s duplicating
contractors, Best Copy and Printing,
Inc., 445 12th Street SW., Room CY–
B402, Washington, DC 20554, telephone
SUMMARY:
E:\FR\FM\13JAP1.SGM
13JAP1
Agencies
[Federal Register Volume 80, Number 8 (Tuesday, January 13, 2015)]
[Proposed Rules]
[Pages 1608-1615]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2015-00328]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R09-OAR-2014-0861, FRL-9921-49-Region 9]
Promulgation of Air Quality Implementation Plans; Arizona;
Regional Haze Federal Implementation Plan; Reconsideration
AGENCY: Environmental Protection Agency.
ACTION: Proposed rule.
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SUMMARY: The Environmental Protection Agency (EPA) is proposing to
revise provisions of the Arizona Regional Haze (RH) Federal
Implementation Plan (FIP) applicable to the Nelson Lime Plant. In
response to a request for reconsideration from the plant's owner,
Lhoist North America of Arizona, Inc. (LNA), we propose to replace the
control technology demonstration requirements for nitrogen oxides
(NOX) applicable to Kilns 1 and 2 at the Nelson Lime Plant
with a series of revised recordkeeping and reporting requirements.
Lastly, we are proposing a correction in the regulatory language of the
final rule where a table listing the pollution emission limits for
NOX and sulfur dioxide (SO2) at each kiln was
misprinted. We are seeking comment on each of these proposed actions.
DATES: Written comments must be submitted on or before February 27,
2015. Requests for a public hearing must be received on or before
January 28, 2015.
ADDRESSES: See the SUPPLEMENTARY INFORMATION section for further
instructions on where and how to learn more about this proposal,
request a public hearing, or submit comments.
FOR FURTHER INFORMATION CONTACT: Thomas Webb, U.S. EPA, Region 9,
Planning Office, Air Division, Air-2, 75 Hawthorne Street, San
Francisco, CA 94105. Thomas Webb can be reached at telephone number
(415) 947-4139 and via electronic mail at webb.thomas@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, ``we,'' ``us,''
and ``our'' refer to EPA.
Table of Contents
I. General Information
II. Background
III. FIP Revision for Nelson Lime Plant
IV. EPA's Proposed Action
V. Statutory and Executive Order Reviews
[[Page 1609]]
I. General Information
A. Definitions
For the purpose of this document, we are giving meaning to certain
words or initials as follows:
The words or initials Act or CAA mean or refer to the
Clean Air Act, unless the context indicates otherwise.
The initials ADEQ mean or refer to the Arizona Department
of Environmental Quality.
The words Arizona and State mean the State of Arizona.
The initials BART mean or refer to Best Available Retrofit
Technology.
The initials CAA mean or refer to the Clean Air Act.
The term Class I area refers to a mandatory Class I
Federal area.\1\
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\1\ Although states and tribes may designate as Class I
additional areas which they consider to have visibility as an
important value, the requirements of the visibility program set
forth in section 169A of the CAA apply only to ``mandatory Class I
Federal areas.''
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The initials CBI mean or refer to Confidential Business
Information.
The initials CEMS mean or refer to continuous emission
monitoring system or systems.
The words EPA, we, us or our mean or refer to the United
States Environmental Protection Agency.
The initials FIP mean or refer to Federal Implementation
Plan.
The initials LNA mean or refer to LNA North America of
Arizona, Inc.
The initials MMBtu mean or refer to million British
thermal units.
The initials NOX mean or refer to nitrogen oxides.
The initials RH mean or refer to regional haze.
The initials RHR mean or refer to EPA's Regional Haze
Rule.
The initials SIP mean or refer to State Implementation
Plan.
The initials SNCR mean or refer to selective non-catalytic
reduction.
The initials SO2 mean or refer to sulfur dioxide.
B. Docket
The proposed action relies on documents, information, and data that
are listed in the index on https://www.regulations.gov under docket
number EPA-R09-OAR-2014-0861. Although listed in the index, some
information is not publicly available (e.g., Confidential Business
Information (CBI)). Certain other material, such as copyrighted
material, is publicly available only in hard copy form. Publicly
available docket materials are available either electronically at
https://www.regulations.gov or in hard copy at the Planning Office of
the Air Division, AIR-2, EPA Region 9, 75 Hawthorne Street, San
Francisco, CA 94105. EPA requests that you contact the individual
listed in the FOR FURTHER INFORMATION CONTACT section to view the hard
copy of the docket. You may view the hard copy of the docket Monday
through Friday, 9-5:00 PDT, excluding Federal holidays.
C. Instructions for Submitting Comments to EPA
Written comments must be submitted on or before February 27, 2015.
Submit your comments, identified by Docket ID No. EPA-R09-OAR-2014-
0861, by one of the following methods:
Federal Rulemaking portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Email: webb.thomas@epa.gov.
Fax: 415-947-3579 (Attention: Thomas Webb).
Mail, Hand Delivery or Courier: Thomas Webb, EPA Region 9,
Air Division (AIR-2), 75 Hawthorne Street, San Francisco, California
94105. Hand and courier deliveries are only accepted Monday through
Friday, 8:30 a.m.-4:30 p.m., excluding Federal holidays. Special
arrangements should be made for deliveries of boxed information.
EPA's policy is to include all comments received in the public
docket without change. We may make comments available online at https://www.regulations.gov, including any personal information provided,
unless the comment includes information claimed to be CBI or other
information for which disclosure is restricted by statute. Do not
submit information that you consider to be CBI or that is otherwise
protected through https://www.regulations.gov or email. The https://www.regulations.gov Web site is an ``anonymous access'' system, which
means EPA will not know your identity or contact information unless you
provide it in the body of your comment. If you send an email comment
directly to EPA, without going through https://www.regulations.gov, we
will include your email address as part of the comment that is placed
in the public docket and made available on the Internet. If you submit
an electronic comment, EPA recommends that you include your name and
other contact information in the body of your comment and with any disk
or CD-ROM you submit. If EPA cannot read your comment due to technical
difficulties and cannot contact you for clarification, EPA may not be
able to consider your comment. Electronic files should not include
special characters or any form of encryption, and be free of any
defects or viruses.
D. Submitting Confidential Business Information
Do not submit CBI to EPA through https://www.regulations.gov or by
email. Clearly mark the part or all of the information that you claim
as CBI. For CBI information in a disk or CD-ROM that you mail to EPA,
mark the outside of the disk or CD-ROM as CBI and identify
electronically within the disk or CD-ROM the specific information that
is claimed as CBI. In addition to one complete version of the comment
that includes information claimed as CBI, you must submit a copy of the
comment that does not contain the information claimed as CBI for
inclusion in the public docket. We will not disclose information so
marked except in accordance with procedures set forth in 40 CFR part 2.
E. Tips for Preparing Your Comments
When submitting comments, remember to:
Identify the rulemaking by docket number and other
identifying information (e.g., subject heading, Federal Register date,
and page number).
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline.
F. Public Hearings
If anyone contacts EPA by January 28, 2015 requesting to speak at a
public hearing, EPA will schedule a public hearing and announce the
hearing in the Federal Register. Contact Thomas Webb at (415) 947-4139
or at webb.thomas@epa.gov to request a hearing or to determine if a
hearing will be held.
II. Background
A. Summary of Statutory and Regulatory Requirements
Congress created a program for protecting visibility in the
nation's national parks and wilderness areas in section 169A of the
1977 Amendments to the CAA. This section of the CAA
[[Page 1610]]
establishes as a national goal the ``prevention of any future, and the
remedying of any existing, impairment of visibility in mandatory Class
I Federal areas which impairment results from man-made air pollution.''
\2\ It also directs states to evaluate the use of retrofit controls at
certain larger, often uncontrolled, older stationary sources in order
to address visibility impacts from these sources. Specifically, section
169A(b)(2)(A) of the CAA requires states to revise their State
Implementation Plans (SIPs) to contain such measures as may be
necessary to make reasonable progress towards the natural visibility
goal, including a requirement that certain categories of existing major
stationary sources built between 1962 and 1977 procure, install, and
operate best available retrofit technology (BART) controls. These
sources are referred to as ``BART-eligible'' sources.\3\ In the 1990
CAA Amendments, Congress amended the visibility provisions in the CAA
to focus attention on the problem of regional haze, which is visibility
impairment produced by a multitude of sources and activities located
across a broad geographic area.\4\ We promulgated the Regional Haze
Rule (RHR) in 1999, which requires states to develop and implement SIPs
to ensure reasonable progress toward improving visibility in mandatory
Class I Federal areas \5\ by reducing emissions that cause or
contribute to regional haze.\6\ Under the Regional Haze Rule (RHR),
states are directed to conduct BART determinations for BART-eligible
sources that may be anticipated to cause or contribute to any
visibility impairment in a Class I area.\7\
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\2\ 42 U.S.C. 7491(a)(1).
\3\ 40 CFR 51.301.
\4\ See CAA section 169B, 42 U.S.C. 7492.
\5\ Areas designated as mandatory Class I Federal areas consist
of national parks exceeding 6000 acres, wilderness areas, and
national memorial parks exceeding 5000 acres, and all international
parks that were in existence on August 7, 1977. 42 U.S.C. 7472(a).
When we use the term ``Class I area'' in this action, we mean a
``mandatory Class I Federal area.''
\6\ See generally 40 CFR 51.308.
\7\ 40 CFR 51.308(e).
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B. History of FIP BART Determination
The Arizona Department of Environmental Quality (ADEQ) submitted a
Regional Haze SIP to EPA on February 28, 2011. EPA promulgated two
final rules approving in part and disapproving in part the Arizona RH
SIP. The first final rule addressed the State's BART determinations for
three power plants (Apache, Cholla, and Coronado).\8\ The second final
rule, which addressed the remaining elements of the Arizona RH SIP,
included our disapproval of the State's determination that the Nelson
Lime Plant was not subject to BART.\9\
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\8\ 77 FR 72512 (December 5, 2012).
\9\ 78 FR 46142 (July 30, 2013).
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In a third final rule, EPA found that the Nelson Lime Plant was
subject to BART and made a BART determination for the plant, as part of
the Arizona RH FIP.\10\ EPA set BART emission limits for NOX
at the Nelson Lime Plant of 3.80 lb/ton of limestone product for Kiln 1
and 2.61 lb/ton of limestone product for Kiln 2 based on a 12-month
rolling average; and a combined limit for Kilns 1 and 2 of 3.27 tons of
NOX/day on a 30-day rolling average. These limits are
consistent with the use of SNCR control technology and represent a 50
percent reduction from baseline emission rates. The FIP also included
monitoring, recordkeeping, and reporting requirements, and established
a compliance deadline for the final NOX emission limits of
September 3, 2017, which is three years from the publication date of
the final rule. Finally, we received certain comments alleging that an
SNCR control efficiency of 50 percent was unsupported, and that SNCR
was capable of achieving control efficiency as high as 80 percent. In
responses to these comments in our final rule, we noted that the
commenters were unable to provide information indicating that an SNCR
control efficiency better than 50 percent was achievable at a lime
kiln. As a result, our final rule established NOX emission
limits consistent with an SNCR control efficiency of 50 percent.
However, in response to these comments, as well as the lack of data
regarding the performance of SNCR on lime kilns, the final rule
included a series of control technology demonstration requirements for
Kiln 1 and Kiln 2 to ensure the optimization of the SNCR systems
installed at the Nelson Lime Plant.
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\10\ 79 FR 52420 (September 3, 2014).
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C. Petition for Reconsideration and Stay
LNA submitted a petition to EPA on October 31, 2014, seeking
administrative reconsideration and a partial stay of the final rule
under CAA section 307(d)(7)(B).\11\ Specifically, LNA requested that
EPA eliminate the control technology demonstration requirements for the
Nelson Lime Plant. In an attachment to the petition, LNA provided
additional data regarding SNCR performance at lime kilns located at
another LNA facility, the O'Neal Lime Plant in Calera, Alabama. In the
petition, LNA also requested a stay if EPA did not take action prior to
December 31, 2014. LNA requested a stay on the grounds that the control
technology demonstration requirements would not provide sufficient time
to meet the SO2 and NOX BART emission limits. LNA
asserted that the time needed to implement the demonstration
requirements, in particular the requirement to collect six months of
uncontrolled NOX emission data, would delay the critical
path schedule for SNCR installation beyond the compliance date. EPA
sent a letter to LNA on November 20, 2014, granting reconsideration of
the optimization protocol requirements pursuant to CAA section
307(d)(7)(B).\12\ Today's notice of proposed rulemaking constitutes
EPA's proposed action on the reconsideration.
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\11\ Letter from Eric Hiser, Jorden Bischoff & Hiser, to Regina
McCarthy, EPA (October 31, 2014).
\12\ Letter from Jared Blumenfeld, EPA to Eric Hiser, Jorden
Bischoff & Hiser (November 20, 2014).
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III. FIP Revision for Nelson Lime Plant
A. Summary of FIP Revision
This proposed rule consists of several components: removal of the
control technology demonstration requirements, revised recordkeeping
and reporting requirements, and an error correction to a table in our
September 3, 2014, final rule. This proposed rule does not change any
of the emission limits, compliance deadlines, or the compliance
determination methods established in the final rule.
B. EPA's Evaluation of Eliminating Control Technology Demonstration
Requirements
EPA is proposing to remove the control technology demonstration
requirements from the final rule based on information provided in LNA's
petition for reconsideration. In particular, in a letter dated October
2, 2014, and enclosed with the petition, LNA provided new data
concerning operation of SNCR at another of its facilities, the O'Neal
Lime Plant. The O'Neal Lime Plant originally consisted of Kiln 1, but
was later expanded through the construction of Kiln 2. In order for the
construction of Kiln 2 not to trigger major new source review for
NOX emissions, LNA elected to install SNCR on both Kilns 1
and 2 to maintain NOX emissions below thresholds for major
new source review. LNA provided information comparing the physical
design of the two kilns at the O'Neal Lime Plant with the two kilns at
the Nelson Lime Plant. LNA indicated that although the two O'Neal kilns
are not identical to the Nelson kilns, O'Neal Kiln 1 is more similar in
design to the Nelson kilns than O'Neal Kiln 2. We consider this
comparison reasonable. Of
[[Page 1611]]
the two O'Neal kilns, Kiln 1 is closer in age, physical dimensions,
lime production rate, and fuel efficiency to the Nelson kilns than Kiln
2.
The remainder of the October 2, 2014, letter summarizes
NOX emission data from specific days of operation at O'Neal
Kiln 1 to evaluate the SNCR control efficiency of the kiln. Evaluating
the control efficiency involves comparing uncontrolled emission rates
with controlled emission rates from Kiln 1. However, uncontrolled
NOX emission data for the O'Neal plant are limited, because
the facility did not operate with a continuous emission monitoring
system (CEMS) for NOX prior to installing SNCR.\13\ As a
result, uncontrolled NOX emission data are limited to those
periods of time following SNCR installation during which the SNCR
system did not operate. LNA provided emission data from six days during
which the SNCR did not operate to represent uncontrolled NOX
emission rates. NOX emission data from those periods
corresponding to hours of SNCR operation were also included as a
representation of controlled NOX emission rates. Based on
this analysis, the SNCR control efficiency of O'Neal Kiln 1 varied from
42 to 61 percent.
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\13\ This is common with older lime and cement plants, and is
similar to the situation at the Nelson plant, which does not
currently operate NOX CEMS.
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This range of control efficiency represents SNCR performance over
relatively short-term periods of less than 24 hours. For example, the
highest observed control efficiency (61 percent) corresponds to a
period ending on December 1, 2011, and consists of a comparison of six
hours of uncontrolled emissions with eight hours of controlled
emissions. As noted in the final rule in regard to control efficiencies
for dry sorbent injection, we do not consider the upper range of short-
term control efficiencies necessarily to be sustainable over longer
periods, such as on an annual average basis.\14\ Therefore, while the
emission data provided by LNA indicate that a 61 percent SNCR control
efficiency was achievable over short term periods (lasting several
hours), we do not necessarily consider 61 percent control efficiency to
be achievable over longer averaging periods, such as an annual average
or 30-day average. For cement kilns, a source category similar to lime
kilns, the highest short-term emission rates can be as much as 25-50
percent greater than the highest annual average or 30-day average
emission rates.\15\ As a result, given the short-term nature of the
emission data indicating a maximum 61 percent SNCR control efficiency,
we consider the use of a 50 percent control efficiency on a longer
annual average basis to be reasonable for the Nelson kilns.
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\14\ 79 FR 52439.
\15\ For comparison, we have examined the maximum 24-hr average,
30-day average, and annual average emissions for Kiln 4 at the
Phoenix Cement Plant (see spreadsheet ``Phoenix Cement Kiln 4
NOX Emissions 2005-10 (public).xlsx.'' The Phoenix Cement
Kiln 4 data illustrate the substantial variability in emission rates
from a cement kiln when examining emissions on short-term versus
longer-term averaging periods. Given the similarity between lime
kilns and cement kilns, we expect similar variability in the short-
term versus longer-term emission rates from lime kilns.
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Accordingly, we propose to find that the data from the O'Neal kilns
are sufficient to establish that an SNCR control efficiency of 50
percent is appropriate for the Nelson kilns for purposes of BART. While
we still consider it necessary to ensure that the SNCR system be
optimized, we do not consider it necessary for LNA to adhere to the
relatively detailed and prescribed procedures contained in the control
technology demonstration requirements. Therefore, we are proposing to
remove the control technology demonstration requirements included in
the final rule, and, as described below, are proposing requirements
that will require LNA to report similar information in a less
prescribed manner.
C. Revised Recordkeeping and Reporting Requirements
We are proposing several additional reporting and recordkeeping
requirements, including a summary of SNCR design and a summary of SNCR
debugging and process improvement activities, to replace the control
technology demonstration requirements in the FIP for Nelson Lime Plant.
As described in III.B above, we consider it necessary to include
provisions for SNCR optimization. Given the NOX emission
data provided by LNA from the O'Neal Plant indicating that 50 percent
SNCR control efficiency has been achieved at a lime kiln, we do not
consider it necessary for optimization measures to be as prescriptive
and detailed as established in our September 4, 2014, final rule.
Specifically, we propose to require LNA to submit a summary of the SNCR
design prior to commencing construction of the ammonia injection system
at Kilns 1 and 2, including information regarding reagent type,
locations selected for reagent injection, reagent injection rate,
equipment arrangement, and kiln characteristics. We also propose to
require LNA to submit a summary of SNCR debugging and process
improvement activities, including a description of each process
adjustment performed on the SNCR system, a discussion of whether the
adjustment affected the NOX emission rate, a description of
the range over which the adjustment was examined, and a discussion of
how the adjustment will be reflected or accounted for in kiln operating
practices.
D. Error Correction
We are proposing a minor correction to a table printed in our
September 3, 2014, final rule at 79 FR 52480. The table, which is
codified at 40 CFR 52.145(i)(3)(i) and lists NOX and
SO2 limits for the Nelson Plant Kilns, appears with
incorrect column labels due to a misprint in the Federal Register. The
table appears with the correct labels in the proposed regulatory text
that follows this proposed rule.
E. Non-interference With Applicable Requirements
The CAA requires that any revision to an implementation plan shall
not be approved by the Administrator if the revision would interfere
with any applicable requirement concerning attainment and reasonable
further progress or any other applicable requirement of the CAA.\16\
Today's proposed revisions would not affect any applicable requirements
of the CAA because they would not alter the amount or timing of
emission reductions from the Nelson Lime Plant. In particular, the
proposed replacement of the control technology demonstration
requirements with a series of recordkeeping and reporting requirements
would not alter any of the applicable emission limitations, compliance
determination methodologies, or compliance deadlines. Therefore, we
propose to find that these revisions would comply with CAA section
110(l).
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\16\ CAA Section 110(l), 42 U.S.C. 7410(l).
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IV. EPA's Proposed Action
For the reasons described above, EPA proposes to revise the Arizona
Regional Haze FIP to eliminate the control technology demonstration
requirements at the Nelson Lime Plant and replace them with additional
recordkeeping and reporting requirements. This revision would
constitute our action on LNA's Petition for Reconsideration of the FIP.
[[Page 1612]]
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This proposed action is not a ``significant regulatory action''
under the terms of Executive Order 12866 (58 FR 51735, October 4, 1993)
and is therefore not subject to review under Executive Orders 12866 and
13563 (76 FR 3821, January 21, 2011). This proposed rule applies to
only one facility and is therefore not a rule of general applicability.
B. Paperwork Reduction Act
This action does not impose an information collection burden under
the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq.
Burden is defined at 5 CFR 1320.3(b).
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA) generally requires an agency
to prepare a regulatory flexibility analysis of any rule subject to
notice and comment rulemaking requirements under the Administrative
Procedure Act or any other statute unless the agency certifies that the
rule will not have a significant economic impact on a substantial
number of small entities. Small entities include small businesses,
small organizations, and small governmental jurisdictions.
For purposes of assessing the impacts of today's proposed rule on
small entities, small entity is defined as: (1) A small business as
defined by the Small Business Administration's (SBA) regulations at 13
CFR 121.201; (2) a small governmental jurisdiction that is a government
of a city, county, town, school district or special district with a
population of less than 50,000; and (3) a small organization that is
any not-for-profit enterprise which is independently owned and operated
and is not dominant in its field. Pursuant to 13 CFR 121.201, footnote
1, a firm is small if it is in NAICS 327410 (lime manufacturing) and
the concern and its affiliates have no more than 500 employees. LNA is
affiliated with the LNA Group, which has more than 5,500 employees.\17\
Therefore, LNA is not a small business.
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\17\ https://www.LNA.com/facts-and-figures-LNA-group-2013.
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D. Unfunded Mandates Reform Act (UMRA)
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), 2
U.S.C. 1531-1538, requires Federal agencies, unless otherwise
prohibited by law, to assess the effects of their regulatory actions on
State, local, and tribal governments and the private sector. Federal
agencies must also develop a plan to provide notice to small
governments that might be significantly or uniquely affected by any
regulatory requirements. The plan must enable officials of affected
small governments to have meaningful and timely input in the
development of EPA regulatory proposals with significant Federal
intergovernmental mandates and must inform, educate, and advise small
governments on compliance with the regulatory requirements.
This proposed rule does not contain a Federal mandate that may
result in expenditures of $100 million or more for state, local, and
tribal governments, in the aggregate, or the private sector in any one
year. Thus, this rule is not subject to the requirements of sections
202 or 205 of UMRA.
This proposed rule is also not subject to the requirements of
section 203 of UMRA because it contains no regulatory requirements that
might significantly or uniquely affect small governments. This proposed
rule does not impose regulatory requirements on any government entity.
E. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the states, on the relationship between
the national government and the states, or in the distribution of power
and responsibilities among the various levels of government, as
specified in Executive Order 13132.
In the spirit of Executive Order 13132, and consistent with EPA
policy to promote communications between EPA and State and local
governments, EPA specifically solicits comment on this proposed action
from State and local officials.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
Under Executive Order 13175 (65 FR 67249, November 9, 2000), EPA
may not issue a regulation that has tribal implications, that imposes
substantial direct compliance costs, and that is not required by
statute, unless the federal government provides the funds necessary to
pay the direct compliance costs incurred by tribal governments, or EPA
consults with tribal officials early in the process of developing the
proposed regulation and develops a tribal summary impact statement.
This proposed rule does not have tribal implications, as specified
in Executive Order 13175. It will not have substantial direct effects
on tribal governments. Thus, Executive Order 13175 does not apply to
this rule. EPA specifically solicits additional comment on this
proposed rule from tribal officials.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
EPA interprets EO 13045 (62 FR 19885, April 23, 1997) as applying
only to those regulatory actions that concern health or safety risks,
such that the analysis required under section 5-501 of the EO has the
potential to influence the regulation. This action is not subject to EO
13045 because it does not establish an environmental standard intended
to mitigate health or safety risks. This proposed action addresses
regional haze and visibility protection.
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not subject to Executive Order 13211 (66 FR 28355
(May 22, 2001)), because it is exempt under Executive Order 12866.
I. National Technology Transfer and Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law 104-113, 12 (10) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus standards (VCS) in its
regulatory activities unless to do so would be inconsistent with
applicable law or otherwise impractical. VCS are technical standards
(e.g., materials specifications, test methods, sampling procedures, and
business practices) that are developed or adopted by the VCS bodies.
The NTTAA directs EPA to provide Congress, through annual reports to
OMB, with explanations when the Agency decides not to use available and
applicable VCS.
EPA believes that VCS are inapplicable to this action. Today's
action does not require the public to perform activities conducive to
the use of VCS.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 12898 (59 FR 7629, February 16, 1994), establishes
federal executive policy on environmental justice. Its main provision
directs
[[Page 1613]]
federal agencies, to the greatest extent practicable and permitted by
law, to make environmental justice part of their mission by identifying
and addressing, as appropriate, disproportionately high and adverse
human health or environmental effects of their programs, policies, and
activities on minority populations and low- income populations in the
United States.
EPA has determined that this proposed rule will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations because it does not
change the level of environmental protection for any affected
populations.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Nitrogen oxides,
Particulate matter, Reporting and recordkeeping requirements, Sulfur
dioxide, Visibility. Incorporation by Reference.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 29, 2014.
Jared Blumenfeld,
Regional Administrator, EPA Region IX.
Part 52, chapter I, title 40 of the Code of Federal Regulations is
proposed to be amended as follows:
PART 52--APPROVAL AND PROMULGATION OF IMPLEMENTATION PLANS
0
1. The authority citation for part 52 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart D--Arizona
0
2. Amend Sec. 52.145 by:
0
a. Revising paragraph (i); and
0
b. Removing Appendix B to Sec. 52.145--Lime Kiln Control Technology
Demonstration Requirements.
The revision reads as follows:
Sec. 52.145 Visibility protection.
* * * * *
(i) Source-specific federal implementation plan for regional haze
at Nelson Lime Plant--
(1) Applicability. This paragraph (i) applies to the owner/operator
of the lime kilns designated as Kiln 1 and Kiln 2 at the Nelson Lime
Plant located in Yavapai County, Arizona.
(2) Definitions. Terms not defined in this paragraph (i)(2) shall
have the meaning given them in the Clean Air Act or EPA's regulations
implementing the Clean Air Act. For purposes of this paragraph (i):
Ammonia injection shall include any of the following: Anhydrous
ammonia, aqueous ammonia, or urea injection.
Continuous emission monitoring system or CEMS means the equipment
required by this section to sample, analyze, measure, and provide, by
means of readings recorded at least once every 15 minutes (using an
automated data acquisition and handling system (DAHS)), a permanent
record of NOX emissions, SO2 emissions, diluent,
and stack gas volumetric flow rate.
Kiln means either of the kilns identified in paragraph (i)(1) of
this section.
Kiln 1 means lime kiln 1, as identified in paragraph (i)(1) of this
section.
Kiln 2 means lime kiln 2, as identified in paragraph (i)(1) of this
section.
Kiln operating day means a 24-hour period between 12 midnight and
the following midnight during which there is operation of Kiln 1, Kiln
2, or both kilns at any time.
Kiln operation means any period when any raw materials are fed into
the Kiln or any period when any combustion is occurring or fuel is
being fired in the Kiln.
Lime product means the product of the lime-kiln calcination
process, including calcitic lime, dolomitic lime, and dead-burned
dolomite.
NOX means oxides of nitrogen.
Owner/operator means any person who owns or who operates, controls,
or supervises a kiln identified in paragraph (i)(1) of this section.
SO2 means sulfur dioxide.
(3) Emission limitations. (i) The owner/operator of the kilns
identified in paragraph (i)(1) of this section shall not emit or cause
to be emitted pollutants in excess of the following limitations in
pounds of pollutant per ton of lime product (lb/ton), from any kiln.
Each emission limit shall be based on a 12-month rolling basis.
Pollutant Emission Limit
------------------------------------------------------------------------
Kiln ID NOX SO[ihel2]
------------------------------------------------------------------------
Kiln 1............................................ 3.80 9.32
Kiln 2............................................ 2.61 9.73
------------------------------------------------------------------------
(ii) The owner/operator of the kilns identified in paragraph (i)(1)
of this section shall not emit or cause to be emitted pollutants in
excess of 3.27 tons of NOX per day and 10.10 tons of
SO2 per day, combined from both kilns, based on a rolling
30-kiln-operating-day basis.
(4) Compliance dates. (i) The owner/operator of each kiln shall
comply with the NOX emission limitations and other
NOX-related requirements of this paragraph (i) no later than
September 4, 2017.
(ii) The owner/operator of each kiln shall comply with the
SO2 emission limitations and other SO2-related
requirements of this paragraph (i) no later than March 3, 2016.
(5) [Reserved]
(6) Compliance determination--(i) Continuous emission monitoring
system. At all times after the compliance dates specified in paragraph
(i)(4) of this section, the owner/operator of kilns 1 and 2 shall
maintain, calibrate, and operate a CEMS, in full compliance with the
requirements found at 40 CFR 60.13 and 40 CFR part 60, appendices B and
F, to accurately measure diluent, stack gas volumetric flow rate, and
concentration by volume of NOX and SO2 emissions
into the atmosphere from kilns 1 and 2. The CEMS shall be used by the
owner/operator to determine compliance with the emission limitations in
paragraph (i)(3) of this section, in combination with data on actual
lime production. The owner/operator must operate the monitoring system
and collect data at all required intervals at all times that an
affected kiln is operating, except for periods of monitoring system
malfunctions, repairs associated with monitoring system malfunctions,
and required monitoring system quality assurance or quality control
activities (including, as applicable, calibration checks and required
zero and span adjustments).
(ii) Ammonia consumption monitoring. Upon and after the completion
of installation of ammonia injection on a kiln, the owner or operator
shall install, and thereafter maintain and operate, instrumentation to
continuously monitor and record levels of ammonia consumption for that
kiln.
(iii) Compliance determination for lb per ton NOX limit. Compliance
with the NOX emission limits described in paragraph
(i)(3)(i) of this section shall be determined based on a rolling 12-
month basis. The 12-month rolling NOX emission rate for each
kiln shall be calculated within 30 days following the end of each
calendar month in accordance with the following procedure: Step one,
sum the hourly pounds of NOX emitted for the month just
completed and the eleven (11) months preceding the month just completed
to calculate the total pounds of NOX emitted over the most
recent twelve (12) month period for that kiln; Step two, sum the total
lime product, in tons, produced during the month just completed and the
eleven (11) months preceding the month just completed to calculate the
total lime product
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produced over the most recent twelve (12) month period for that kiln;
Step three, divide the total amount of NOX calculated from
Step one by the total lime product calculated from Step two to
calculate the 12-month rolling NOX emission rate for that
kiln. Each 12-month rolling NOX emission rate shall include
all emissions and all lime product that occur during all periods within
the 12-month period, including emissions from startup, shutdown, and
malfunction.
(iv) Compliance determination for lb per ton SO2 limit. Compliance
with the SO2 emission limits described in paragraph
(i)(3)(i) of this section shall be determined based on a rolling 12-
month basis. The 12-month rolling SO2 emission rate for each
kiln shall be calculated within 30 days following the end of each
calendar month in accordance with the following procedure: Step one,
sum the hourly pounds of SO2 emitted for the month just
completed and the eleven (11) months preceding the month just completed
to calculate the total pounds of SO2 emitted over the most
recent twelve (12) month period for that kiln; Step two, sum the total
lime product, in tons, produced during the month just completed and the
eleven (11) months preceding the month just completed to calculate the
total lime product produced over the most recent twelve (12) month
period for that kiln; Step three, divide the total amount of
SO2 calculated from Step one by the total lime product
calculated from Step two to calculate the 12-month rolling
SO2 emission rate for that kiln. Each 12-month rolling
SO2 emission rate shall include all emissions and all lime
product that occur during all periods within the 12-month period,
including emissions from startup, shutdown, and malfunction.
(v) Compliance determination for ton per day NOX limit. Compliance
with the NOX emission limit described in paragraph
(i)(3)(ii) of this section shall be determined based on a rolling 30-
kiln-operating-day basis. The rolling 30-kiln operating day
NOX emission rate for the kilns shall be calculated for each
kiln operating day in accordance with the following procedure: Step
one, sum the hourly pounds of NOX emitted from both kilns
for the current kiln operating day and the preceding twenty-nine (29)
kiln-operating-day period for both kilns; Step two, divide the total
pounds of NOX calculated from Step one by two thousand
(2,000) to calculate the total tons of NOX; Step three,
divide the total tons of NOX calculated from Step two by
thirty (30) to calculate the rolling 30-kiln operating day
NOX emission rate for both kilns. Each rolling 30-kiln
operating day NOX emission rate shall include all emissions
that occur from both kilns during all periods within any kiln operating
day, including emissions from startup, shutdown, and malfunction.
(vi) Compliance determination for ton per day SO2 limit. Compliance
with the SO2 emission limit described in paragraph
(i)(3)(ii) of this section shall be determined based on a rolling 30-
kiln-operating-day basis. The rolling 30-kiln operating day
SO2 emission rate for the kilns shall be calculated for each
kiln operating day in accordance with the following procedure: Step
one, sum the hourly pounds of SO2 emitted from both kilns
for the current kiln operating day and the preceding twenty-nine (29)
kiln operating days, to calculate the total pounds of SO2
emitted over the most recent thirty (30) kiln operating day period for
both kilns; Step two, divide the total pounds of SO2
calculated from Step one by two thousand (2,000) to calculate the total
tons of SO2; Step three, divide the total tons of
SO2 calculated from Step two by thirty (30) to calculate the
rolling 30-kiln operating day SO2 emission rate for both
kilns. Each rolling 30-kiln operating day SO2 emission rate
shall include all emissions that occur from both kilns during all
periods within any kiln operating day, including emissions from
startup, shutdown, and malfunction.
(7) Recordkeeping. The owner/operator shall maintain the following
records for at least five years:
(i) All CEMS data, including the date, place, and time of sampling
or measurement; parameters sampled or measured; and results.
(ii) All records of lime production.
(iii) Monthly rolling 12-month emission rates of NOX and
SO2, calculated in accordance with paragraphs (i)(6)(iii)
and (iv) of this section.
(iv) Daily rolling 30-kiln operating day emission rates of
NOX and SO2 calculated in accordance with
paragraphs (i)(6)(v) and (vi) of this section.
(v) Records of quality assurance and quality control activities for
emissions measuring systems including, but not limited to, any records
specified by 40 CFR part 60, appendix F, Procedure 1, as well as the
following:
(A) The occurrence and duration of any startup, shutdown, or
malfunction, performance testing, evaluations, calibrations, checks,
adjustments maintenance, duration of any periods during which a CEMS or
COMS is inoperative, and corresponding emission measurements.
(B) Date, place, and time of measurement or monitoring equipment
maintenance activity;
(C) Operating conditions at the time of measurement or monitoring
equipment maintenance activity;
(D) Date, place, name of company or entity that performed the
measurement or monitoring equipment maintenance activity and the
methods used; and
(E) Results of the measurement or monitoring equipment maintenance.
(vi) Records of ammonia consumption, as recorded by the
instrumentation required in paragraph (i)(6)(ii) of this section.
(vii) Records of all major maintenance activities conducted on
emission units, air pollution control equipment, CEMS, and lime
production measurement devices.
(viii) All other records specified by 40 CFR part 60, appendix F,
Procedure 1.
(8) Reporting. All reports required under this section shall be
submitted by the owner/operator to the Director, Enforcement Division,
U.S. Environmental Protection Agency, Region 9, electronically via
email to aeo_r9@epa.gov. Any data that are required under this section
shall be submitted in Excel format. Reports required under paragraphs
(i)(8)(iii) through (i)(8)(v) of this section shall be submitted within
30 days after the applicable compliance date(s) in paragraph (i)(4) of
this section and at least semiannually thereafter, within 30 days after
the end of a semiannual period. The owner/operator may submit reports
more frequently than semiannually for the purposes of synchronizing
reports required under this section with other reporting requirements,
such as the title V monitoring report required by 40 CFR
70.6(a)(3)(iii)(A), but at no point shall the duration of a semiannual
period exceed six months.
(i) Prior to commencing construction of the ammonia injection
system, the owner/operator shall submit to EPA a summary report of the
design of the SNCR system. Elements of this summary report shall
include: Reagent type, description of the locations selected for
reagent injection, reagent injection rate (expressed as a molar ratio
of reagent to NOX), equipment list, equipment arrangement,
and a summary of kiln characteristics that were relied upon as the
design basis for the SNCR system.
(ii) By October 3, 2017, the owner/operator shall submit to EPA a
summary of any process improvement or debugging activities that were
performed on the SNCR system.
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Elements of this summary report shall include: A description of each
process adjustment performed on the SNCR system, a discussion of
whether the adjustment affected NOX emission rate (including
CEMS data that may have been recorded while the adjustment was in
progress), a description of the range (if applicable) over which the
adjustment was examined, and a discussion of how the adjustment will be
reflected or accounted for in kiln operating practices. In addition, to
the extent that the owner/operator evaluates the impact of varying
reagent injection rate on NOX emissions, the owner/operator
shall include the following information: The range of reagent injection
rates evaluated (expressed as a molar ratio of reagent to average
NOX concentration), reagent injection rate, average
NOX concentration, lime production rate, kiln flue gas
temperature, and the presence of any detached plumes from the kiln
exhaust.
(iii) The owner/operator shall submit a report that lists the daily
rolling 30-kiln operating day emission rates for NOX and
SO2, calculated in accordance with paragraphs (i)(6)(iii)
and (iv) of this section.
(iv) The owner/operator shall submit a report that lists the
monthly rolling 12-month emission rates for NOX and
SO2, calculated in accordance with paragraphs (i)(6)(v) and
(vi) of this section.
(v) The owner/operator shall submit excess emissions reports for
NOX and SO2 limits. Excess emissions means
emissions that exceed any of the emissions limits specified in
paragraph (i)(3) of this section. The reports shall include the
magnitude, date(s), and duration of each period of excessemissions;
specific identification of each period of excess emissions that occurs
during startups, shutdowns, and malfunctions of the kiln; the nature
and cause of any malfunction (if known); and the corrective action
taken or preventative measures adopted.
(vi) The owner/operator shall submit a summary of CEMS operation,
to include dates and duration of each period during which the CEMS was
inoperative (except for zero and span adjustments and calibration
checks), reason(s) why the CEMS was inoperative and steps taken to
prevent recurrence, and any CEMS repairs or adjustments.
(vii) The owner/operator shall submit results of all CEMS
performance tests required by 40 CFR part 60, Appendix F, Procedure 1
(Relative Accuracy Test Audits, Relative Accuracy Audits, and Cylinder
Gas Audits).
(viiii) When no excess emissions have occurred or the CEMS has not
been inoperative, repaired, or adjusted during the reporting period,
the owner/operator shall state such information in the semiannual
report.
(9) Notifications. All notifications required under this section
shall be submitted by the owner/operator to the Director, Enforcement
Division (Mail Code ENF-2-1), U.S. Environmental Protection Agency,
Region 9, 75 Hawthorne Street, San Francisco, California 94105-3901.
(i) The owner/operator shall submit notification of commencement of
construction of any equipment which is being constructed to comply with
the NOX emission limits in paragraph (i)(3) of this section.
(ii) The owner/operator shall submit semiannual progress reports on
construction of any such equipment.
(iii) The owner/operator shall submit notification of initial
startup of any such equipment.
(10) Equipment operations. (i) At all times, including periods of
startup, shutdown, and malfunction, the owner/operator shall, to the
extent practicable, maintain and operate the kilns, including
associated air pollution control equipment, in a manner consistent with
good air pollution control practices for minimizing emissions.
Pollution control equipment shall be designed and capable of operating
properly to minimize emissions during all expected operating
conditions. Determination of whether acceptable operating and
maintenance procedures are being used will be based on information
available to the Regional Administrator, which may include, but is not
limited to, monitoring results, review of operating and maintenance
procedures, and inspection of the kilns.
(ii) After completion of installation of ammonia injection on a
kiln, the owner/operator shall inject sufficient ammonia to achieve
compliance with the NOX emission limits from paragraph
(i)(3) of this section for that kiln while preventing excessive ammonia
emissions.
(11) Enforcement. Notwithstanding any other provision in this
implementation plan, any credible evidence or information relevant as
to whether the kiln would have been in compliance with applicable
requirements if the appropriate performance or compliance test had been
performed can be used to establish whether or not the owner/operator
has violated or is in violation of any standard or applicable emission
limit in the plan.
[FR Doc. 2015-00328 Filed 1-12-15; 8:45 am]
BILLING CODE 6560-50-P