Standards of Performance for Fossil-Fuel-Fired Steam Generators for Which Construction Is Commenced After August 17, 1971; Standards of Performance for Electric Utility Steam Generating Units for Which Construction Is Commenced After September 18, 1978; Standards of Performance for Industrial-Commercial-Institutional Steam Generating Units; and Standards of Performance for Small Industrial-Commercial-Institutional Steam Generating Units, 5072-5093 [E9-523]
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40 CFR Part 60
[EPA–HQ–OAR–2005–0031; FRL–8748–2]
RIN 2060–AO61
SUPPLEMENTARY INFORMATION:
EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2005–0031. All
documents in the docket are listed in
the Federal Docket Management System
index at https://www.regulations.gov.
Although listed in the index, some
information is not publicly available,
e.g. , confidential business information
or other information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically through https://
www.regulations.gov or in hard copy at
the EPA Docket Center, Public Reading
Room, EPA West, Room 3334, 1301
Constitution Ave., NW., Washington,
DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
Docket is (202) 566–1742.
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this
document?
C. Judicial Review
II. Background Information
III. Final Amendments and Response to
Public Comments
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
ADDRESSES:
Standards of Performance for FossilFuel-Fired Steam Generators for Which
Construction Is Commenced After
August 17, 1971; Standards of
Performance for Electric Utility Steam
Generating Units for Which
Construction Is Commenced After
September 18, 1978; Standards of
Performance for IndustrialCommercial-Institutional Steam
Generating Units; and Standards of
Performance for Small IndustrialCommercial-Institutional Steam
Generating Units
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Final rule.
SUMMARY: EPA is amending the new
source performance standards (NSPS)
for electric utility steam generating units
and industrial-commercial-institutional
steam generating units. These
amendments to the regulations are to
add compliance alternatives for owners
and operators of certain affected
sources, eliminate the opacity standard
for facilities with a particulate matter
(PM) limit of 0.030 lb/million British
thermal units (MMBtu) or less that
choose to voluntarily install and use PM
continuous emission monitors (CEMS)
to demonstrate compliance with that
limit, and to correct technical and
editorial errors.
FOR FURTHER INFORMATION CONTACT: Mr.
Christian Fellner, Energy Strategies
Group, Sector Policies and Programs
Division (D243–01), U.S. EPA, Research
Triangle Park, NC 27711, telephone
number (919) 541–4003, facsimile
number (919) 541–5450, electronic mail
NAICS Code1
Category
Industry .....................................................
Federal Government .................................
221112
22112
State/local/ tribal government ...................
22112
921150
211
Any industrial, commercial, or institutional
facility using a steam generating unit as
defined in 60.40b or 60.4c.
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321
322
325
324
316, 326, 339
331
332
336
221
622
611
1 North
(e-mail) address:
fellner.christian@epa.gov.
DATES: This final rule is effective on
January 28, 2009. The incorporation by
reference of certain publications listed
in this final rule is approved by the
Director of the Federal Register as of
January 28, 2009.
ENVIRONMENTAL PROTECTION
AGENCY
Outline.
The information presented in this
preamble is organized as follows:
I. General Information
A. Does this action apply to me?
The regulated categories and entities
potentially affected by this final action
include, but are not limited to, the
following:
Examples of potentially regulated entities
Fossil fuel-fired electric utility steam generating units.
Fossil fuel-fired electric utility steam generating units owned by the Federal Government.
Fossil fuel-fired electric utility steam generating units owned by municipalities.
Fossil fuel-fired electric steam generating units in Indian Country.
Extractors of crude petroleum and natural gas.
Manufacturers of lumber and wood products.
Pulp and paper mills.
Chemical manufacturers.
Petroleum refiners and manufacturers of coal products.
Manufacturers of rubber and miscellaneous plastic products.
Steel works, blast furnaces.
Electroplating, plating, polishing, anodizing, and coloring.
Manufacturers of motor vehicle parts and accessories.
Electric, gas, and sanitary services.
Health services.
Educational services.
American Industry Classification System (NAICS) code.
This table is not intended to be
exhaustive, but rather provides a guide
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for readers regarding entities likely to be
regulated by this action. To determine
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whether your facility is regulated by this
action, you should examine the
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applicability criteria in § 60.40, § 60.40a,
§ 60.40b, or § 60.40c of 40 CFR part 60.
If you have any questions regarding the
applicability of this action to a
particular entity, consult either the air
permit authority for the entity or your
EPA regional representative as listed in
§ 63.13 of subpart A (General
Provisions) of title 40 of the Code of
Federal Regulations.
B. Where can I get a copy of this
document?
In addition to being available in the
docket, an electronic copy of this final
action will also be available on the
Worldwide Web (WWW) through the
Technology Transfer Network (TTN).
Following signature, a copy of this final
action will be posted on the TTN’s
policy and guidance page for newly
proposed or promulgated rules at the
following address: https://www.epa.gov/
ttn/oarpg/. The TTN provides
information and technology exchange in
various areas of air pollution control.
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C. Judicial Review
Under section 307(b)(1) of the Clean
Air Act (CAA), judicial review of these
final rules is available only by filing a
petition for review in the U.S. Court of
Appeals for the District of Columbia
Circuit by March 30, 2009. Under
section 307(d)(7)(B) of the CAA, only an
objection to these final rules that was
raised with reasonable specificity
during the period for public comment
can be raised during judicial review.
Moreover, under section 307(b)(2) of the
CAA, the requirements established by
these final rules may not be challenged
separately in any civil or criminal
proceedings brought by EPA to enforce
these requirements.
II. Background Information
In response to petitions for
reconsideration of the amendments to
the new source performance standards
for steam generating units that EPA
promulgated on June 13, 2007 (72 FR
32710) filed by the Coke Oven
Environmental Task Force, EPA
proposed revised amendments to
address issues for which the petitioners
requested reconsideration (see docket
entry EPA–HQ–OAR–2005–0031–0276).
EPA also proposed certain other
unrelated amendments it felt were
appropriate. In sum, EPA proposed on
June 12, 2008 (73 FR 33642) to amend
subparts D, Da, Db, and Dc of 40 CFR
part 60 to clarify the intent for applying
and implementing specific rule
requirements, provide additional
compliance alternatives, and to correct
unintentional technical omissions and
editorial errors.
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A 45-day comment period (June 12,
2008 to July 28, 2008) was provided to
accept comments on the proposed rule.
An opportunity for a public hearing was
provided to allow any interested
persons to present oral comments on the
proposed rule. However, EPA did not
receive a request for a formal public
hearing, so a public hearing was not
held. We received comments on the
proposed amendments from 11
commenters during the comment
period.
III. Final Amendments and Response to
Public Comments
We are amending subparts D, Da, Db,
and Dc of 40 CFR part 60 to add
compliance alternatives for owners/
operators of certain affected sources, to
eliminate the opacity standard for
certain facilities voluntarily using PM
CEMS, and to correct technical and
editorial errors. These amendments
address issues raised by the Coke Oven
Environmental Task Force, including an
alternate sulfur dioxide (SO2) limit
during SO2 control system maintenance
and allowing the use of parametric
monitoring of nitrogen oxide (NOX)
emissions for owners and operators of
coke oven gas-fired (COG) steam
generating units. In addition, we are
specifying the opacity monitoring
requirements for owners and operators
of all affected facilities that are subject
to an opacity limit, including owner and
operators of COG-fired steam generating
units, but exempt from the continuous
opacity monitoring system (COMS)
requirement. This action promulgates
the amended regulatory language as
proposed, except for those significant
provisions identified below.
We are also finalizing several
clarifications to correct technical and
editorial errors and to amend the
monitoring requirements for owners and
operators of affected facilities that elect
to install particulate matter continuous
emission monitoring systems (PM
CEMS). Owners and operators of
affected facilities that install a PM
CEMS will be exempt from the opacity
standard as long as they are complying
with a federally enforceable permit
limiting PM emissions to 0.030 pounds
per million British thermal units or less.
In addition, owner and operators of
affected facilities that elect to install PM
CEMS will be required to measure and
report emissions of condensable PM.
Minor revisions to the proposed
regulatory language were also made to
clarify specific provisions or to correct
unintentional technical omissions and
terminology, typographical, printing,
and grammatical errors that were
identified in the proposed rule either as
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a result of comments we received or
based on our own subsequent review of
the text. One change revises appropriate
definitions and requirements in subpart
Da to clarify the applicability and
implementation of the subpart Da
provisions to integrated coal gasification
combined cycle electric utility power
plants. Another change clarifies the fact
that not all combined cycle facilities
that burn solid derived fuels are subject
to the subpart.
The final amendments promulgated
by this action reflect EPA’s
consideration of the comments received
on the proposal. EPA’s responses to the
substantive public comments on the
proposal are presented in a comment
summary and response document
available in Docket ID No. EPA–HQ–
OAR–2005–0031. A summary of
selected public comments and our
responses is as follows.
Comment: Several commenters
generally support the exemption of
affected facilities using PM CEMS from
the opacity standard. However, the
commenters requested that EPA exempt
those affected facilities opting to use PM
CEMS from the opacity standard
without imposing conditions for
additional condensable PM or opacity
tests. The commenters stated the EPA’s
proposed method for measuring
condensable PM (Method 202) is flawed
and significantly overstates the amount
of condensable PM, and noted that
Method 202 itself condenses gaseous
emissions that would not be condensing
in the flue gas. They also noted that
further improvements of Method 202
must be made before it is required as the
method to measure condensable PM.
Response: The opacity standard and
all opacity monitoring requirements
have been eliminated for owner/
operators of affected facilities
complying with a federally enforceable
PM limit of 0.030 lb/MMBtu or less who
voluntarily elect to use a PM CEMS to
demonstrate continuous compliance
with the PM limit. The contribution of
filterable PM to opacity at these
emission levels is generally negligible,
and sources with mass limits at this
level or less will operate with little or
no visible emissions (i.e. less than 5
percent opacity). As a result, EPA
believes that an opacity standard is no
longer necessary for these sources since
the PM mass emission rate standard is
substantially tighter than the opacity
standard and the mass of PM emissions
will be continually monitored.
We concluded, however, that it is
only appropriate to eliminate the
opacity standard and associated opacity
monitoring for owners/operators of
facilities complying with a PM limit of
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0.030 lb/MMBtu or less. At this
emission rate, the presence of visible
emissions may indicate that the PM
control device is not operating properly.
This amended NSPS does not require
any corrective action in such a case as
long as the PM CEMS is complying with
all applicable federal requirements.
However, PM CEMS readings cannot be
verified as readily as other CEMS, and
since recalibration requires PM
performance tests, baseline opacity
readings can be a valuable secondary
check on control device performance
and PM emissions. The local permitting
authority does have the discretion to
require an investigation to determine
the cause of the visible emissions. The
presence of such emissions is not,
however, necessarily evidence of a
violation of the PM standard. In
situations where the owner/operator of
a facility has documented visible
emissions during the initial or
subsequent PM CEMS calibration testing
or documented trends in PM CEMS
readings that correlate to the visible
emissions, the relative amount of visible
emissions can still be used by the local
permitting authority as a secondary
check that both the PM control device
and PM CEMS are operating properly.
While these facilities will not be
required to install continuous opacity
monitoring systems (COMS), if a facility
decided to or is required by the
permitting authority to install a COMS,
the data would be useful as a secondary
check on PM emissions and proper
operation of the PM control device and
to verify that the PM CEMS is operating
properly. Owners/operators of affected
facilities with a PM limit greater than
0.030 lb/MMBtu that elect to install PM
CEMS may have some visible emissions,
will still be subject to an opacity limit,
and will be required to either use a
COMS or perform periodic visual
inspections to comply with the opacity
standard.
In addition, we have concluded it is
appropriate to require condensable PM
testing for owners/operators of affected
facilities that elect to use PM CEMS to
determine the contribution of
condensable PM to total PM emissions.
We will use this data to determine if the
condensable PM emissions from steam
generating units have a significant
health and/or environmental impact and
whether condensable PM should be
included in future amendments to the
PM standard. By early 2009, we intend
to propose amendments to Method 202
that will address the concerns about
artifact measurement. Since the rule
will not be finalized until early in 2010,
we are delaying the requirement to
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perform condensable PM testing until
July 1, 2010 or until Method 202 is
revised to minimize artifact
measurement, whichever is later.
Comment: Several commenters
oppose increasing the Method 9
monitoring frequency. The commenters
stated that increasing the frequency
from annually to a weekly, monthly, or
quarterly basis without identifying any
particular issue of concern that might
occur on a weekly, monthly, or
quarterly basis is arbitrary, unnecessary,
overly burdensome, and would provide
little environmental benefit. In addition,
one commenter supports the use of
Method 22 as an alternative to Method
9 for those sources that are expected to
have no significant visible emissions.
However, three 1-hour Method 22
observations would actually take
significantly longer than 3 hours. Under
Method 22, observers are instructed not
to continuously view emissions for
more than 15–20 minutes at a time, and
that breaks of 5–10 minutes should be
taken between each observation.
Following these criteria, each 1-hour
observation would take at least one and
a half hours. Finally, one commenter
requested that EPA allow for owners/
operators of affected facilities that
comply with subpart D, Da, Db, or Dc,
by the use of a fabric filter, the
alternative of installing and operating
triboelectric bag leak detectors as an
alternative to using a COMS.
Response: We have concluded that
the appropriate approach is to base the
frequency of visible emissions
monitoring on the level of visible
emissions detected during the most
recent observation. Owners/operators of
facilities that elect to not use a COMS
to demonstrate compliance with the
opacity limit will conduct at least an
initial Method 9 performance test. The
frequency of the required subsequent
Method 9 testing is based on the results
of the highest 6-minute opacity
observed during the most recent
performance test. Owners/operators of
affected facilities where the maximum
6-minute opacity reading is greater than
10 percent will be required to conduct
monthly Method 9 performance testing;
owners/operators of affected facilities
where the maximum 6-minute opacity
reading is between 5 percent and 10
percent will be required to conduct
quarterly Method 9 performance testing;
owners/operators of affected facilities
with some visible emissions but where
the maximum 6-minute opacity reading
is 5 percent or less will be required to
conduct semi-annual Method 9
performance testing; and owners/
operators of affected facilities with no
visible emissions will only be required
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to conduct an annual Method 9
performance test.
As an alternative, owners/operators of
affected facilities where maximum 6minute opacity readings from the most
recent Method 9 performance test is less
than 10 percent may elect to use either
Method 22 or the digital opacity
monitoring system in lieu of subsequent
Method 9 performance testing. The
proposed amendments required a total
of 3 hours of observation annually, but
did not specify when or for how long
those observations would be done. We
have concluded it is appropriate to
decrease the length of each observation
to a minimum of 10 minutes, but to
increase the frequency to daily
observations. This approach both
minimizes the burden of this option
while increasing protection to the
environment, as observations will be
performed throughout the year. If an
owner/operator of an affected facility
observes visible emissions in excess of
5 percent during any observation and is
unable to take corrective action, they
will be required to either conduct a
Method 9 performance test with the
previously specified frequency or to
install a COMS. To maintain
consistency in the operation of the
digital opacity monitoring system, the
EPA Administrator will approve opacity
monitoring plans for owners/operators
that elect to use the digital opacity
monitoring system to detect the
presence of visible emissions.
Finally, we have concluded it is
appropriate to allow owners/operators
of affected facilities subject to subparts
Da, Db, and Dc, and who install,
maintain, and operate a bag leak
detection system, the option to use
periodic visual inspections of plume
opacity as an alternative to monitoring
opacity with a COMS. Modern
baghouses often operate with no visible
emissions, and a bag leak detection
system will allow owners/operators to
identify potential problems with the
control device and repair the problems
prior to increases in opacity.
Comment: Several commenters
oppose the proposed requirement to
electronically submit performance
evaluation test date to EPA’s WebFIRE
database. One commenter stated that
EPA has not: (1) Provided any rationale
for requiring the data to be reported and
entered electronically; (2) provided any
information on the proposed reporting
format or mechanism to allow interested
parties to understand what sort of
burden this requirement would impose
and whether the requirement is more or
less burdensome than other forms of
reporting; or (3) provided any
mechanism for sources to confirm the
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authenticity of data submitted to this
Web site for their facility. Furthermore,
before EPA can impose any new
reporting requirement, EPA must
comply with the requirements of the
Paperwork Reduction Act and also
address whether the submission meets
the requirements of the Cross-Media
Electronic Reporting Rule (CROMERR),
which is codified at 40 CFR part 3.
Another commenter stated that any
reporting should not be required of
sources until the WebFIRE is fully
operational. A formal regulation is not
the proper venue to ‘‘troubleshoot’’
communications with an external
database for the regulated community.
Response: EPA does not expect
WebFIRE and the associated Electronic
Reporting Tool (ERT) to be operational
until early 2011, and we are delaying
the requirement until July 1, 2011. We
do not expect electronic submittal of
performance test information to have
any significant costs or impacts to
industry (because we are not requiring
additional testing or software and
source testing companies already
compile these data electronically), and
since submission of data directly to EPA
is only a requirement for facilities that
voluntary elect to use PM CEMS to
demonstrate compliance with the PM
limit, the ICR does not need to be
amended. In addition, as an alternate to
using the ERT we are allowing owner/
operators to mail the test report directly
to EPA. Finally, we fully expect the ERT
to be compliant with CROMERR before
reporting is required in 2011.
Comment: Two commenters requested
that EPA reconsider the Agency’s
decision to include direct contact water
heaters in the definition of ‘‘steam
generating unit’’ used for determining
applicability of the requirements under
subparts Db and Dc because it is
contrary to previous EPA applicability
determinations, and it is confusing to
include water heaters in a regulation for
steam generating units.
Response: The definition of steam
generating unit includes direct contact
water heaters and as such, these units
meet the applicability of subpart Dc.
However, we recognize that two sourcespecific letters exempt individual direct
contact water heaters from the
applicability of subpart Dc of 40 CFR
part 60, and owners/operators of the
units in question reasonably relied on
these determinations and have not been
complying with subpart Dc to date. We
do not intend to reverse these source
specific determinations or to require
retroactive reporting for any owner/
operators of similar facilities that relied
on these determinations and have not
been maintaining the proper records,
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but we are clarifying and confirming
that direct contact water heaters have
always been subject to subpart Dc, and
records shall be maintained from June
12, 2008 onward, consistent with the
definition of steam generating unit.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
‘‘significant regulatory action’’ because
it may raise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Accordingly, EPA submitted this action
to the Office of Management and Budget
(OMB) for review under Executive
Order 12866 and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. The final
rule results in no changes to the
information collection requirements of
the existing standards of performance
and will have no impact on the
information collection estimate of
projected cost and hour burden made
and approved by the OMB during the
development of the existing standards of
performance. Therefore, the information
collection requests have not been
amended. However, OMB previously
approved the information collection
requirements contained in the existing
regulations (subparts Da, Db, and Dc of
40 CFR part 60) under the provisions of
the Paperwork Reduction Act, 44 U.S.C.
3501 et seq., and has assigned OMB
control numbers 2060–0023 for subpart
Da of 40 CFR part 60, 2060–0072 for
subpart Db of 40 CFR part 60, and 2060–
0202 for subpart Dc of 40 CFR part 60.
OMB control numbers for EPA’s
regulations in 40 CFR are listed in 40
CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
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.
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For purposes of assessing the impacts
of the final amendments on small
entities, small entity is defined as: (1) A
small business as defined by the Small
Business Administration’s 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.
After considering the economic
impacts of this final rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
In determining whether a rule has a
significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the rule
on small entities.’’ 5 U.S.C. 603 and 604.
Thus, an agency may certify that a rule
will not have a significant economic
impact on a substantial number of small
entities if the rule relieves regulatory
burden, or otherwise has a positive
economic effect on all of the small
entities subject to the rule.
EPA is minimizing the opacity
monitoring requirements for owner/
operators of affected facilities subject to
an opacity standard but exempt from the
COMS requirement. We have therefore
concluded that this final rule will
relieve regulatory burden for all affected
small entities.
D. Unfunded Mandates Reform Act
This rule does not change the overall
cost of the rule and therefore does not
contain a Federal mandate that may
result in expenditures of $100 million or
more for State, local, and trial
governments, in the aggregate, or the
private sector in any 1 year. Thus, this
final rule is not subject to the
requirements of sections 202 or 205 of
UMRA.
This 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
rule modifies previously established
requirements and does not impose any
new obligations or enforceable duties on
any small governments.
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E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’
This final rule 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 on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This action will
not impose substantial direct
compliance costs on State or local
governments; it will not preempt State
law. Thus, Executive Order 13132 does
not apply to this rule.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). While utility steam generating
units are located on tribal lands, EPA is
not aware of any that are owned by
tribal governments. Thus, Executive
Order 13175 does not apply to this
action.
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G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
EPA interprets Executive Order 13045
(62 FR 19885, April 23, 1997) as
applying to those regulatory actions that
concern health or safety risks, such that
the analysis required under section 5–
501 of the Executive Order has the
potential to influence the regulation.
This action is not subject to Executive
Order 13045 because it is based solely
on technology performance.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (66 FR 28355, May 22,
2001) because it is not likely to have a
significant adverse effect on the supply,
distribution, or use of energy. We have
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concluded that this final rule is not
likely to have any adverse energy effects
because it generally only clarifies our
intent and corrects errors in the existing
rule.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113 (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. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. NTTAA directs EPA
to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards.
This final rule involves technical
standards. EPA has decided to use
ASTM D975–08a, ‘‘Standard
Specification for Diesel Fuel Oils,’’ for
defining diesel fuel oil. This standard is
available from the American Society for
Testing and Materials (ASTM), 100 Barr
Harbor Drive, Post Office Box C700,
West Conshohocken, PA 19428–2959.
EPA has also decided to use EPA
Method 202 (40 CFR part 51, appendix
M). The Agency has not found any
alternative methods. The search and
review results are in the docket for this
regulation.
Under 40 CFR 60.13(i) of the NSPS
General Provisions, a source may apply
to EPA for permission to use alternative
test methods or alternative monitoring
requirements in place of any required
testing methods, performance
specifications, or procedures in the final
rule and amendments.
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
Federal agencies, to the greatest extent
practical 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.
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EPA has determined that this final
rule will not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations because it does
not affect the level of protection
provided to human health or the
environment. This action does not
change any emission limits and,
therefore, does not affect the level of
protection provided to human health or
the environment.
H. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801, et seq., as added by the
Small Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing these final
amendments and other required
information to the U.S. Senate, the U.S.
House of Representatives, and the
Comptroller General of the United
States prior to publication of the final
rules in the Federal Register. A major
rule cannot take effect until 60 days
after it is published in the Federal
Register. This action is not a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2). This
final rule will be effective on January
28, 2009.
List of Subjects in 40 CFR Part 60
Environmental protection,
Administrative practice and procedure,
Air pollution control, Incorporation by
reference, Intergovernmental relations,
Reporting and recordkeeping
requirements.
Dated: November 26, 2008.
Stephen L. Johnson,
Administrator.
Editorial Note: This document was
received in the Office of the Federal Register
on Thursday, January 8, 2009.
For the reasons stated in the preamble,
title 40, chapter I, part 60 of the Code
of Federal Regulations is amended as
follows:
■
PART 60—[AMENDED]
1. The authority citation for part 60
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart A—[Amended]
2. Section 60.17 is amended by
redesignating paragraphs (a)(17) through
(a)(92) as paragraphs (a)(18) through
(a)(93) and by adding new paragraph
(a)(17) to read as follows:
■
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§ 60.17
Incorporations by Reference.
*
*
*
*
*
(a) * * *
(17) ASTM D975–08a, Standard
Specification for Diesel Fuel Oils, IBR
approved for §§ 60.41b of subpart Db of
this part and 60.41c of subpart Dc of this
part.
*
*
*
*
*
Subpart D—[Amended]
3. Section 60.42 is amended by adding
paragraph (c) to read as follows:
■
§ 60.42
(PM).
Standard for particulate matter
*
*
*
*
*
(c) As an alternate to meeting the
requirements of paragraph (a) of this
section, an owner or operator that elects
to install, calibrate, maintain, and
operate a continuous emissions
monitoring systems (CEMS) for
measuring PM emissions can petition
the Administrator (in writing) to comply
with § 60.42Da(a) of subpart Da of this
part. If the Administrator grants the
petition, the source will from then on
(unless the unit is modified or
reconstructed in the future) have to
comply with the requirements in
§ 60.43Da(a) of subpart Da of this part.
■ 4. Section 60.43 is amended by
revising paragraph (d) to read as
follows:
*
*
*
*
*
§ 60.43
Standard for sulfur dioxide (SO2).
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(d) As an alternate to meeting the
requirements of paragraphs (a) and (b) of
this section, an owner or operator can
petition the Administrator (in writing)
to comply with § 60.43Da(i)(3) of
subpart Da of this part or comply with
§ 60.42b(k)(4) of subpart Db of this part,
as applicable to the affected source. If
the Administrator grants the petition,
the source will from then on (unless the
unit is modified or reconstructed in the
future) have to comply with the
requirements in § 60.43Da(i)(3) of
subpart Da of this part or § 60.42b(k)(4)
of subpart Db of this part, as applicable
to the affected source.
■ 5. Section 60.45 is amended to read as
follows:
■ a. By revising paragraph (a);
■ b. By revising paragraphs (b)(1) and
(b)(6)(i)(C) and adding paragraph (b)(7);
■ c. By revising paragraphs (g)(2), (g)(3),
and (g)(4); and
■ d. By adding paragraph (h).
§ 60.45
Emissions and fuel monitoring.
(a) Each owner or operator shall
install, calibrate, maintain, and operate
continuous opacity monitoring system
(COMS) for measuring opacity and a
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CEMS for measuring SO2 emissions,
NOX emissions, and either oxygen (O2)
or carbon dioxide (CO2) except as
provided in paragraph (b) of this
section.
(b) * * *
(1) For a fossil-fuel-fired steam
generator that burns only gaseous or
liquid fossil fuel (excluding residual oil)
with potential SO2 emissions rates of 26
ng/J (0.060 lb/MMBtu) or less and that
does not use post-combustion
technology to reduce emissions of SO2
or PM, CEMS for measuring the opacity
of emissions and SO2 emissions are not
required if the owner or operator
monitors SO2 emissions by fuel
sampling and analysis or fuel receipts.
*
*
*
*
*
(6) * * *
(i) * * *
(C) At a minimum, valid 1-hour CO
emissions averages must be obtained for
at least 90 percent of the operating
hours on a 30-day rolling average basis.
The 1-hour averages are calculated
using the data points required in
§ 60.13(h)(2).
*
*
*
*
*
(7) The owner or operator of an
affected facility subject to an opacity
standard under § 60.42 and that elects to
not install a COMS because the affected
facility burns only fuels as specified
under paragraph (b)(1) of this section,
monitors PM emissions as specified
under paragraph (b)(5) of this section, or
monitors CO emissions as specified
under paragraph (b)(6) of this section
shall conduct a performance test using
Method 9 of appendix A–4 of this part
and the procedures in § 60.11 to
demonstrate compliance with the
applicable limit in § 60.42 and shall
comply with either paragraphs (b)(7)(i),
(b)(7)(ii), or (b)(7)(iii) of this section. If
during the initial 60 minutes of
observation all 6-minute averages are
less than 10 percent and all individual
15-second observations are less than or
equal to 20 percent, the observation
period may be reduced from 3 hours to
60 minutes.
(i) Except as provided in paragraph
(b)(7)(ii) or (b)(7)(iii) of this section, the
owner or operator shall conduct
subsequent Method 9 of appendix A–4
of this part performance tests using the
procedures in paragraph (b)(7) of this
section according to the applicable
schedule in paragraphs (b)(7)(i)(A)
through (b)(7)(i)(D) of this section, as
determined by the most recent Method
9 of appendix A–4 of this part
performance test results.
(A) If no visible emissions are
observed, a subsequent Method 9 of
appendix A–4 of this part performance
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test must be completed within 12
calendar months from the date that the
most recent performance test was
conducted;
(B) If visible emissions are observed
but the maximum 6-minute average
opacity is less than or equal to 5
percent, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 6
calendar months from the date that the
most recent performance test was
conducted;
(C) If the maximum 6-minute average
opacity is greater than 5 percent but less
than or equal to 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 3 calendar months
from the date that the most recent
performance test was conducted; or
(D) If the maximum 6-minute average
opacity is greater than 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 30 calendar days from
the date that the most recent
performance test was conducted.
(ii) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 of this part performance
test, elect to perform subsequent
monitoring using Method 22 of
appendix A–7 of this part according to
the procedures specified in paragraphs
(b)(7)(ii)(A) and (B) of this section.
(A) The owner or operator shall
conduct 10 minute observations (during
normal operation) each operating day
the affected facility fires fuel for which
an opacity standard is applicable using
Method 22 of appendix A–7 of this part
and demonstrate that the sum of the
occurrences of any visible emissions is
not in excess of 5 percent of the
observation period (i.e., 30 seconds per
10 minute period). If the sum of the
occurrence of any visible emissions is
greater than 30 seconds during the
initial 10 minute observation,
immediately conduct a 30 minute
observation. If the sum of the
occurrence of visible emissions is
greater than 5 percent of the observation
period (i.e., 90 seconds per 30 minute
period) the owner or operator shall
either document and adjust the
operation of the facility and
demonstrate within 24 hours that the
sum of the occurrence of visible
emissions is equal to or less than 5
percent during a 30 minute observation
(i.e., 90 seconds) or conduct a new
Method 9 of appendix A–4 of this part
performance test using the procedures
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in paragraph (b)(7) of this section within
30 calendar days according to the
requirements in § 60.46(b)(3).
(B) If no visible emissions are
observed for 30 operating days during
which an opacity standard is applicable,
observations can be reduced to once
every 7 operating days during which an
opacity standard is applicable. If any
visible emissions are observed, daily
observations shall be resumed.
(iii) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 performance tests, elect
to perform subsequent monitoring using
a digital opacity compliance system
according to a site-specific monitoring
plan approved by the Administrator.
The observations shall be similar, but
not necessarily identical, to the
requirements in paragraph (b)(7)(ii) of
this section. For reference purposes in
preparing the monitoring plan, see
OAQPS ‘‘Determination of Visible
Emission Opacity from Stationary
Sources Using Computer-Based
Photographic Analysis Systems.’’ This
document is available from the U.S.
Environmental Protection Agency (U.S.
EPA); Office of Air Quality and
Planning Standards; Sector Policies and
Programs Division; Measurement Policy
Group (D243–02), Research Triangle
Park, NC 27711. This document is also
available on the Technology Transfer
Network (TTN) under Emission
Measurement Center Preliminary
Methods.
*
*
*
*
*
(g) * * *
(2) Sulfur dioxide. Excess emissions
for affected facilities are defined as:
(i) For affected facilities electing not
to comply with § 60.43(d), any threehour period during which the average
emissions (arithmetic average of three
contiguous one-hour periods) of SO2 as
measured by a CEMS exceed the
applicable standard in § 60.43; or
(ii) For affected facilities electing to
comply with § 60.43(d), any 30
operating day period during which the
average emissions (arithmetic average of
all one-hour periods during the 30
operating days) of SO2 as measured by
a CEMS exceed the applicable standard
in § 60.43. Facilities complying with the
30-day SO2 standard shall use the most
current associated SO2 compliance and
monitoring requirements in §§ 60.48Da
and 60.49Da of subpart Da of this part
or §§ 60.45b and 60.47b of subpart Db of
this part, as applicable.
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(3) Nitrogen oxides. Excess emissions
for affected facilities using a CEMS for
measuring NOX are defined as:
(i) For affected facilities electing not
to comply with § 60.44(e), any threehour period during which the average
emissions (arithmetic average of three
contiguous one-hour periods) exceed
the applicable standards in § 60.44; or
(ii) For affected facilities electing to
comply with § 60.44(e), any 30
operating day period during which the
average emissions (arithmetic average of
all one-hour periods during the 30
operating days) of NOX as measured by
a CEMS exceed the applicable standard
in § 60.44. Facilities complying with the
30-day NOX standard shall use the most
current associated NOX compliance and
monitoring requirements in §§ 60.48Da
and 60.49Da of subpart Da of this part.
(4) Particulate matter. Excess
emissions for affected facilities using a
CEMS for measuring PM are defined as
any boiler operating day period during
which the average emissions (arithmetic
average of all operating one-hour
periods) exceed the applicable
standards in § 60.42. Affected facilities
using PM CEMS must follow the most
current applicable compliance and
monitoring provisions in §§ 60.48Da
and 60.49Da of subpart Da of this part.
(h) The owner or operator of an
affected facility subject to the opacity
limits in § 60.42 that elects to monitor
emissions according to the requirements
in § 60.45(b)(7) shall maintain records
according to the requirements specified
in paragraphs (h)(1) through (3) of this
section, as applicable to the visible
emissions monitoring method used.
(1) For each performance test
conducted using Method 9 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(h)(1)(i) through (iii) of this section.
(i) Dates and time intervals of all
opacity observation periods;
(ii) Name, affiliation, and copy of
current visible emission reading
certification for each visible emission
observer participating in the
performance test; and
(iii) Copies of all visible emission
observer opacity field data sheets;
(2) For each performance test
conducted using Method 22 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(h)(2)(i) through (iv) of this section.
(i) Dates and time intervals of all
visible emissions observation periods;
(ii) Name and affiliation for each
visible emission observer participating
in the performance test;
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(iii) Copies of all visible emission
observer opacity field data sheets; and
(iv) Documentation of any
adjustments made and the time the
adjustments were completed to the
affected facility operation by the owner
or operator to demonstrate compliance
with the applicable monitoring
requirements.
(3) For each digital opacity
compliance system, the owner or
operator shall maintain records and
submit reports according to the
requirements specified in the sitespecific monitoring plan approved by
the Administrator.
■ 6. Section 60.46 is amended by
revising paragraph (d)(2) to read as
follows:
§ 60.46
Test methods and procedures.
*
*
*
*
*
(d) * * *
(2) For Method 5 or 5B of appendix
A–3 of this part, Method 17 of appendix
A–6 of this part may be used at facilities
with or without wet FGD systems if the
stack gas temperature at the sampling
location does not exceed an average
temperature of 160 °C (320 °F). The
procedures of sections 8.1 and 11.1 of
Method 5B of appendix A–3 of this part
may be used with Method 17 of
appendix A–6 of this part only if it is
used after wet FGD systems. Method 17
of appendix A–6 of this part shall not
be used after wet FGD systems if the
effluent gas is saturated or laden with
water droplets.
*
*
*
*
*
Subpart Da—[Amended]
7. Section 60.40Da is amended by
revising paragraphs (a) and (b), and
adding paragraph (e) to read as follows:
■
§ 60.40Da Applicability and designation of
affected facility.
(a) Except as specified in paragraph
(e) of this section, the affected facility to
which this subpart applies is each
electric utility steam generating unit:
(1) That is capable of combusting
more than 73 megawatts (MW) (250
million British thermal units per hour
(MMBtu/hr)) heat input of fossil fuel
(either alone or in combination with any
other fuel); and
(2) For which construction,
modification, or reconstruction is
commenced after September 18, 1978.
(b) An IGCC electric utility steam
generating unit (both the stationary
combustion turbine and any associated
duct burners) is subject to this part and
is not subject to subpart GG or KKKK of
this part if both of the conditions
specified in paragraphs (b)(1) and (2) of
this section are met.
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(1) The IGCC electric utility steam
generating unit is capable of combusting
more than 73 MW (250 MMBtu/hr) heat
input of fossil fuel (either alone or in
combination with any other fuel); and
(2) The IGCC electric utility steam
generating unit commenced
construction, modification, or
reconstruction after February 28, 2005.
*
*
*
*
*
(e) Applicability of the requirement of
this subpart to an electric utility
combined cycle gas turbine other than
an IGCC electric utility steam generating
unit is as specified in paragraphs (e)(1)
and (2) of this section.
(1) Heat recovery steam generators
used with duct burners and associated
with an electric utility combined cycle
gas turbine that are capable of
combusting more than 73 MW (250
MMBtu/hr) heat input of fossil fuel are
subject to this subpart except in cases
when the heat recovery steam generator
meets the applicability requirements
and is subject to subpart KKKK of this
part.
(2) For heat recovery steam generators
use with duct burners subject to this
subpart, only emissions resulting from
the combustion of fuels in the steam
generating unit (i.e. duct burners) are
subject to the standards under this
subpart. (The emissions resulting from
the combustion of fuels in the stationary
combustion turbine engine are subject to
subpart GG or KKK, as applicable, of
this part).
■ 8. Section 60.41Da is amended by
revising the definitions of ‘‘Gross
output,’’ ‘‘Integrated gasification
combined cycle electric utility steam
generating unit or IGCC electric utility
steam generating unit,’’ ‘‘Natural gas,’’
and ‘‘Petroleum’’ to read as follows:
§ 60.41Da
Definitions.
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*
*
*
*
*
Gross output means the gross useful
work performed by the steam generated
and, for an IGCC electric utility steam
generating unit, the work performed by
the stationary combustion turbines. For
a unit generating only electricity, the
gross useful work performed is the gross
electrical output from the unit’s turbine/
generator sets. For a cogeneration unit,
the gross useful work performed is the
gross electrical or mechanical output
plus 75 percent of the useful thermal
output measured relative to ISO
conditions that is not used to generate
additional electrical or mechanical
output or to enhance the performance of
the unit (i.e., steam delivered to an
industrial process).
*
*
*
*
*
Integrated gasification combined
cycle electric utility steam generating
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unit or IGCC electric utility steam
generating unit means an electric utility
combined cycle gas turbine that is
designed to burn fuels containing 50
percent (by heat input) or more solidderived fuel not meeting the definition
of natural gas. No solid fuel is directly
burned in the unit during operation.
Natural gas means:
(1) A naturally occurring mixture of
hydrocarbon and nonhydrocarbon gases
found in geologic formations beneath
the earth’s surface, of which the
principal constituent is methane; or
(2) Liquid petroleum gas, as defined
by the American Society of Testing and
Materials in ASTM D1835 (incorporated
by reference, see § 60.17); or
(3) A mixture of hydrocarbons that
maintains a gaseous state at ISO
conditions. Additionally, natural gas
must either be composed of at least 70
percent methane by volume or have a
gross calorific value between 34 and 43
megajoules (MJ) per dry standard cubic
meter (910 and 1,150 Btu per dry
standard cubic foot).
*
*
*
*
*
Petroleum means crude oil or a fuel
derived from crude oil, including, but
not limited to, distillate oil, and residual
oil.
*
*
*
*
*
■ 9. Section 60.42Da is amended by
revising paragraph (b) to read as follows:
§ 60.42Da
(PM).
Standard for particulate matter
*
*
*
*
*
(b) On and after the date the initial
PM performance test is completed or
required to be completed under § 60.8,
whichever date comes first, no owner or
operator subject to the provisions of this
subpart shall cause to be discharged into
the atmosphere from any affected
facility any gases which exhibit greater
than 20 percent opacity (6-minute
average), except for one 6-minute period
per hour of not more than 27 percent
opacity. Owners and operators of an
affected facility that elect to install,
calibrate, maintain, and operate a
continuous emissions monitoring
system (CEMS) for measuring PM
emissions according to the requirements
of this subpart are exempt from the
opacity standard specified in this
paragraph b.
*
*
*
*
*
■ 10. Section 60.48Da is amended to
read as follows:
■ a. By revising paragraph (g)(3);
■ b. By revising the first sentence of
paragraph (j)(2);
■ c. By revising paragraph (n);
■ d. By revising paragraph (o)
introductory text;
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e. By revising paragraph (o)(1);
f. By revising paragraph (o)(2)(ii);
g. By revising the last sentence of
paragraph (o)(2)(iii);
■ h. By revising paragraphs (o)(2)(iv)
and (o)(2)(vi);
■ i. By revising paragraphs (o)(3)(i) and
(o)(3)(ii);
■ j. By revising the first sentence of
paragraph (o)(3)(iii);
■ k. By revising the last sentence of
paragraph (o)(3)(v);
■ l. By revising paragraph (o)(4)(i)(E);
■ m. By revising the first sentence of
paragraph (o)(4)(ii);
■ n. By revising paragraphs (o)(4)(ii)(F),
(o)(4)(v) and (o)(4)(5);
■ o. By revising paragraph (p)
introductory text and (p)(2); and
■ p. By adding paragraph (q).
■
■
■
§ 60.48Da
Compliance provisions.
*
*
*
*
*
(g) * * *
(3) Compliance with applicable daily
average PM emission limitations is
determined by calculating the
arithmetic average of all hourly
emission rates for PM each boiler
operating day, except for data obtained
during startup, shutdown, and
malfunction. Averages are only
calculated for boiler operating days that
have valid data for at least 18 hours of
unit operation during which the
standard applies. Instead, all of the
valid hourly emission rates of the
operating day(s) not meeting the
minimum 18 hours valid data daily
average requirement are averaged with
all of the valid hourly emission rates of
the next boiler operating day with 18
hours or more of valid PM CEMS data
to determine compliance.
*
*
*
*
*
(j) * * *
(2) The owner or operator of an
affected duct burner may elect to
determine compliance by using the
CEMS specified under § 60.49Da for
measuring NOX and oxygen (O2) (or
carbon dioxide (CO2)) and meet the
requirements of § 60.49Da. * * *
*
*
*
*
*
(n) Compliance provisions for sources
subject to § 60.42Da(c)(1). The owner or
operator of an affected facility subject to
§ 60.42Da(c)(1) shall calculate PM
emissions by multiplying the average
hourly PM output concentration
(measured according to the provisions
of § 60.49Da(t)), by the average hourly
flow rate (measured according to the
provisions of § 60.49Da(l) or
§ 60.49Da(m)), and divided by the
average hourly gross energy output
(measured according to the provisions
of § 60.49Da(k)). Compliance with the
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emission limit is determined by
calculating the arithmetic average of the
hourly emission rates computed for
each boiler operating day.
(o) Compliance provisions for sources
subject to § 60.42Da(c)(2) or (d). Except
as provided for in paragraph (p) of this
section, the owner or operator of an
affected facility for which construction,
reconstruction, or modification
commenced after February 28, 2005,
shall demonstrate compliance with each
applicable emission limit according to
the requirements in paragraphs (o)(1)
through (o)(5) of this section.
(1) You must conduct a performance
test to demonstrate initial compliance
with the applicable PM emissions limit
in § 60.42Da(c)(2) or (d) by the
applicable date specified in § 60.8(a).
Thereafter, you must conduct each
subsequent performance test within 12
calendar months following the date the
previous performance test was required
to be conducted. You must conduct
each performance test according to the
requirements in § 60.8 using the test
methods and procedures in § 60.50Da.
The owner or operator of an affected
facility that has not operated for 60
consecutive calendar days prior to the
date that the subsequent performance
test would have been required had the
unit been operating is not required to
perform the subsequent performance
test until 30 calendar days after the next
boiler operating day. Requests for
additional 30 day extensions shall be
granted by the relevant air division or
office director of the appropriate
Regional Office of the U.S. EPA.
(2) * * *
(ii) You must comply with the quality
assurance requirements in paragraphs
(o)(2)(ii)(A) through (E) of this section.
*
*
*
*
*
(iii) * * * If your opacity baseline
level is less than 5.0 percent, then the
opacity baseline level is set at 5.0
percent.
(iv) You must evaluate the preceding
24-hour average opacity level measured
by the COMS each boiler operating day
excluding periods of affected facility
startup, shutdown, or malfunction. If
the measured 24-hour average opacity
emission level is greater than the
baseline opacity level determined in
paragraph (o)(2)(iii) of this section, you
must initiate investigation of the
relevant equipment and control systems
within 24 hours of the first discovery of
the high opacity incident and take the
appropriate corrective action as soon as
practicable to adjust control settings or
repair equipment to reduce the
measured 24-hour average opacity to a
level below the baseline opacity level.
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In cases when a wet scrubber is used in
combination with another PM control
device that serves as the primary PM
control device, the wet scrubber must be
maintained and operated.
*
*
*
*
*
(vi) If the measured 24-hour average
opacity for your affected facility remains
at a level greater than the opacity
baseline level after 7 boiler operating
days, then you must conduct a new PM
performance test according to paragraph
(o)(1) of this section and establish a new
opacity baseline value according to
paragraph (o)(2) of this section. This
new performance test must be
conducted within 60 days of the date
that the measured 24-hour average
opacity was first determined to exceed
the baseline opacity level unless a
waiver is granted by the permitting
authority.
(3) * * *
(i) You must calibrate the ESP
predictive model with each PM control
device used to comply with the
applicable PM emissions limit in
§ 60.42Da(c)(2) or (d) operating under
normal conditions. In cases when a wet
scrubber is used in combination with an
ESP to comply with the PM emissions
limit, the wet scrubber must be
maintained and operated.
(ii) You must develop a site-specific
monitoring plan that includes a
description of the ESP predictive model
used, the model input parameters, and
the procedures and criteria for
establishing monitoring parameter
baseline levels indicative of compliance
with the PM emissions limit. You must
submit the site-specific monitoring plan
for approval by the permitting authority.
For reference purposes in preparing the
monitoring plan, see the OAQPS
‘‘Compliance Assurance Monitoring
(CAM) Protocol for an Electrostatic
Precipitator (ESP) Controlling
Particulate Matter (PM) Emissions from
a Coal-Fired Boiler.’’ This document is
available from the U.S. Environmental
Protection Agency (U.S. EPA); Office of
Air Quality Planning and Standards;
Sector Policies and Programs Division;
Measurement Policy Group (D243–02),
Research Triangle Park, NC 27711. This
document is also available on the
Technology Transfer Network (TTN)
under Emission Measurement Center
Continuous Emission Monitoring.
(iii) You must run the ESP predictive
model using the applicable input data
each boiler operating day and evaluate
the model output for the preceding
boiler operating day excluding periods
of affected facility startup, shutdown, or
malfunction. * * *
*
*
*
*
*
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(v) * * * This new performance test
must be conducted within 60 calendar
days of the date that the model
parameter was first determined to
exceed its baseline level unless a waiver
is granted by the permitting authority.
(4) * * *
(i) * * *
(E) Following initial adjustment, you
must not adjust the averaging period,
alarm set point, or alarm delay time
without approval from the permitting
authority except as provided in
paragraph (d)(1)(vi) of this section.
*
*
*
*
*
(ii) You must develop and submit to
the permitting authority for approval a
site-specific monitoring plan for each
bag leak detection system. * * *
*
*
*
*
*
(F) Corrective action procedures as
specified in paragraph (o)(4)(iii) of this
section. In approving the site-specific
monitoring plan, the permitting
authority may allow owners and
operators more than 3 hours to alleviate
a specific condition that causes an alarm
if the owner or operator identifies in the
monitoring plan this specific condition
as one that could lead to an alarm,
adequately explains why it is not
feasible to alleviate this condition
within 3 hours of the time the alarm
occurs, and demonstrates that the
requested time will ensure alleviation of
this condition as expeditiously as
practicable.
*
*
*
*
*
(v) If after any period composed of 30
boiler operating days during which the
alarm rate exceeds 5 percent of the
process operating time (excluding
control device or process startup,
shutdown, and malfunction), then you
must conduct a new PM performance
test according to paragraph (o)(1) of this
section. This new performance test must
be conducted within 60 calendar days of
the date that the alarm rate was first
determined to exceed 5 percent limit
unless a waiver is granted by the
permitting authority.
(5) An owner or operator of a
modified affected facility electing to
meet the emission limitations in
§ 60.42Da(d) shall determine the percent
reduction in PM by using the emission
rate for PM determined by the
performance test conducted according
to the requirements in paragraph (o)(1)
of this section and the ash content on a
mass basis of the fuel burned during
each performance test run as
determined by analysis of the fuel as
fired.
(p) As an alternative to meeting the
compliance provisions specified in
paragraph (o) of this section, an owner
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or operator may elect to install,
evaluate, maintain, and operate a CEMS
measuring PM emissions discharged
from the affected facility to the
atmosphere and record the output of the
system as specified in paragraphs (p)(1)
through (p)(8) of this section.
*
*
*
*
*
(2) Each CEMS shall be installed,
evaluated, operated, and maintained
according to the requirements in
§ 60.49Da(v).
*
*
*
*
*
(q) Compliance provisions for sources
subject to § 60.42Da(b). An owner or
operator of an affected facility subject to
the opacity standard in § 60.42Da(b)
shall monitor the opacity of emissions
discharged from the affected facility to
the atmosphere according to the
requirements in § 60.49Da(a), as
applicable to the affected facility.
■ 11. Section 60.49Da is amended to
read as follows:
■ a. By revising paragraph (a);
■ b. By revising paragraphs (b)(4)
introductory text and (b)(4)(iii);
■ c. By revising paragraph (d);
■ d. By revising paragraph (i)(3);
■ e. By revising paragraph (k)
introductory text;
■ f. By revising paragraph (t);
■ g. By revising paragraph (u);
■ h. By revising paragraphs (v)
introductory text and (v)(2), and adding
paragraph (v)(4); and
■ j. By adding paragraph (w)
introductory text;
■ k. By revising paragraphs (w)(1) and
(w)(2).
sroberts on PROD1PC70 with RULES
§ 60.49Da
Emission monitoring.
(a) An owner or operator of an
affected facility subject to the opacity
standard in § 60.42Da(b) shall monitor
the opacity of emissions discharged
from the affected facility to the
atmosphere according to the applicable
requirements in paragraphs (a)(1)
through (3) of this section.
(1) Except as provided for in
paragraph (a)(2) of this section, the
owner or operator of an affected facility,
shall install, calibrate, maintain, and
operate a COMS, and record the output
of the system, for measuring the opacity
of emissions discharged to the
atmosphere. If opacity interference due
to water droplets exists in the stack (for
example, from the use of an FGD
system), the opacity is monitored
upstream of the interference (at the inlet
to the FGD system). If opacity
interference is experienced at all
locations (both at the inlet and outlet of
the SO2 control system), alternate
parameters indicative of the PM control
system’s performance and/or good
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combustion are monitored (subject to
the approval of the Administrator).
(2) As an alternative to the monitoring
requirements in paragraph (a)(1) of this
section, an owner or operator of an
affected facility that meets the
conditions in either paragraph (a)(2)(i),
(ii), or (iii) of this section may elect to
monitor opacity as specified in
paragraph (a)(3) of this section.
(i) The affected facility uses a fabric
filter (baghouse) to meet the standards
in § 60.42Da and a bag leak detection
system is installed and operated
according to the requirements in
paragraphs § 60.48Da(o)(4)(i) through
(v);
(ii) The affected facility burns only
gaseous or liquid fuels (excluding
residual oil) with potential SO2
emissions rates of 26 ng/J (0.060 lb/
MMBtu) or less, and does not use a postcombustion technology to reduce
emissions of SO2 or PM; or
(iii) The affected facility meets all of
the conditions specified in paragraphs
(a)(2)(iii)(A) through (C) of this section.
(A) No post-combustion technology
(except a wet scrubber) is used for
reducing PM, SO2, or carbon monoxide
(CO) emissions;
(B) Only natural gas, gaseous fuels, or
fuel oils that contain less than or equal
to 0.30 weight percent sulfur are
burned; and
(C) Emissions of CO discharged to the
atmosphere are maintained at levels less
than or equal to 1.4 lb/MWh on a boiler
operating day average basis as
demonstrated by the use of a CEMS
measuring CO emissions according to
the procedures specified in paragraph
(u) of this section.
(3) The owner or operators of an
affected facility that meets the
conditions in paragraph (a)(2) of this
section may, as an alternative to COMS,
elect to monitor visible emissions using
the applicable procedures specified in
paragraphs (a)(3)(i) through (iv) of this
section.
(i) The owner or operator shall
conduct a performance test using
Method 9 of appendix A–4 of this part
and the procedures in § 60.11. If during
the initial 60 minutes of the observation
all the 6-minute averages are less than
10 percent and all the individual 15second observations are less than or
equal to 20 percent, then the
observation period may be reduced from
3 hours to 60 minutes.
(ii) Except as provided in paragraph
(a)(3)(iii) or (iv) of this section, the
owner or operator shall conduct
subsequent Method 9 of appendix A–4
of this part performance tests using the
procedures in paragraph (a)(3)(i) of this
section according to the applicable
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schedule in paragraphs (a)(3)(ii)(A)
through (a)(3)(ii)(D) of this section, as
determined by the most recent Method
9 of appendix A–4 of this part
performance test results.
(A) If no visible emissions are
observed, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 12
calendar months from the date that the
most recent performance test was
conducted;
(B) If visible emissions are observed
but the maximum 6-minute average
opacity is less than or equal to 5
percent, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 6
calendar months from the date that the
most recent performance test was
conducted;
(C) If the maximum 6-minute average
opacity is greater than 5 percent but less
than or equal to 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 3 calendar months
from the date that the most recent
performance test was conducted; or
(D) If the maximum 6-minute average
opacity is greater than 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 30 calendar days from
the date that the most recent
performance test was conducted.
(iii) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 of this part performance
tests, elect to perform subsequent
monitoring using Method 22 of
appendix A–7 of this part according to
the procedures specified in paragraphs
(a)(3)(iii)(A) and (B) of this section.
(A) The owner or operator shall
conduct 10 minute observations (during
normal operation) each operating day
the affected facility fires fuel for which
an opacity standard is applicable using
Method 22 of appendix A–7 of this part
and demonstrate that the sum of the
occurrences of any visible emissions is
not in excess of 5 percent of the
observation period (i.e., 30 seconds per
10 minute period). If the sum of the
occurrence of any visible emissions is
greater than 30 seconds during the
initial 10 minute observation,
immediately conduct a 30 minute
observation. If the sum of the
occurrence of visible emissions is
greater than 5 percent of the observation
period (i.e., 90 seconds per 30 minute
period) the owner or operator shall
either document and adjust the
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operation of the facility and
demonstrate within 24 hours that the
sum of the occurrence of visible
emissions is equal to or less than 5
percent during a 30 minute observation
(i.e., 90 seconds) or conduct a new
Method 9 of appendix A–4 of this part
performance test using the procedures
in paragraph (a)(3)(i) of this section
within 30 calendar days according to
the requirements in § 60.50Da(b)(3).
(B) If no visible emissions are
observed for 30 operating days during
which an opacity standard is applicable,
observations can be reduced to once
every 7 operating days during which an
opacity standard is applicable. If any
visible emissions are observed, daily
observations shall be resumed.
(iv) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 performance tests, elect
to perform subsequent monitoring using
a digital opacity compliance system
according to a site-specific monitoring
plan approved by the Administrator.
The observations shall be similar, but
not necessarily identical, to the
requirements in paragraph (a)(3)(iii) of
this section. For reference purposes in
preparing the monitoring plan, see
OAQPS ‘‘Determination of Visible
Emission Opacity from Stationary
Sources Using Computer-Based
Photographic Analysis Systems.’’ This
document is available from the U.S.
Environmental Protection Agency (U.S.
EPA); Office of Air Quality and
Planning Standards; Sector Policies and
Programs Division; Measurement Policy
Group (D243–02), Research Triangle
Park, NC 27711. This document is also
available on the Technology Transfer
Network (TTN) under Emission
Measurement Center Preliminary
Methods.
(b) * * *
(4) If the owner or operator has
installed and certified a SO2 CEMS
according to the requirements of
§ 75.20(c)(1) of this chapter and
appendix A to part 75 of this chapter,
and is continuing to meet the ongoing
quality assurance requirements of
§ 75.21 of this chapter and appendix B
to part 75 of this chapter, that CEMS
may be used to meet the requirements
of this section, provided that:
*
*
*
*
*
(iii) The reporting requirements of
§ 60.51Da are met. The SO2 and, if
required, CO2 (or O2) data reported to
meet the requirements of § 60.51Da shall
not include substitute data values
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derived from the missing data
procedures in subpart D of part 75 of
this chapter, nor shall the SO2 data have
been bias adjusted according to the
procedures of part 75 of this chapter.
*
*
*
*
*
(d) The owner or operator of an
affected facility not complying with an
output based limit shall install,
calibrate, maintain, and operate a
CEMS, and record the output of the
system, for measuring the O2 or carbon
dioxide (CO2) content of the flue gases
at each location where SO2 or NOX
emissions are monitored. For affected
facilities subject to a lb/MMBtu SO2
emission limit under § 60.43Da, if the
owner or operator has installed and
certified a CO2 or O2 monitoring system
according to § 75.20(c) of this chapter
and appendix A to part 75 of this
chapter and the monitoring system
continues to meet the applicable
quality-assurance provisions of § 75.21
of this chapter and appendix B to part
75 of this chapter, that CEMS may be
used together with the part 75 SO2
concentration monitoring system
described in paragraph (b) of this
section, to determine the SO2 emission
rate in lb/MMBtu. SO2 data used to meet
the requirements of § 60.51Da shall not
include substitute data values derived
from the missing data procedures in
subpart D of part 75 of this chapter, nor
shall the data have been bias adjusted
according to the procedures of part 75
of this chapter.
*
*
*
*
*
(i) * * *
(3) For affected facilities burning only
fossil fuel, the span value for a COMS
is between 60 and 80 percent. Span
values for a CEMS measuring NOX shall
be determined using one of the
following procedures:
*
*
*
*
*
(k) The procedures specified in
paragraphs (k)(1) through (3) of this
section shall be used to determine gross
output for sources demonstrating
compliance with the output-based
standard under §§ 60.42Da(c),
60.43Da(i), 60.43Da(j), 60.44Da(d)(1),
and 60.44Da(e).
*
*
*
*
*
(t) The owner or operator of an
affected facility demonstrating
compliance with the output-based
emissions limitation under
§ 60.42Da(c)(1) shall install, certify,
operate, and maintain a CEMS for
measuring PM emissions according to
the requirements of paragraph (v) of this
section. An owner or operator of an
affected facility demonstrating
compliance with the input-based
emission limitation in § 60.42Da(a)(1) or
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§ 60.42Da(c)(2) may install, certify,
operate, and maintain a CEMS for
measuring PM emissions according to
the requirements of paragraph (v) of this
section.
(u) The owner or operator of an
affected facility using a CEMS
measuring CO emissions to meet
requirements of this subpart shall meet
the requirements specified in
paragraphs (u)(1) through (4) of this
section.
(1) You must monitor CO emissions
using a CEMS according to the
procedures specified in paragraphs
(u)(1)(i) through (iv) of this section.
(i) The CO CEMS must be installed,
certified, maintained, and operated
according to the provisions in
§ 60.58b(i)(3) of subpart Eb of this part.
(ii) Each 1-hour CO emissions average
is calculated using the data points
generated by the CO CEMS expressed in
parts per million by volume corrected to
3 percent oxygen (dry basis).
(iii) At a minimum, valid 1-hour CO
emissions averages must be obtained for
at least 90 percent of the operating
hours on a 30-day rolling average basis.
The 1-hour averages are calculated
using the data points required in
§ 60.13(h)(2).
(iv) Quarterly accuracy
determinations and daily calibration
drift tests for the CO CEMS must be
performed in accordance with
procedure 1 in appendix F of this part.
(2) You must calculate the 1-hour
average CO emissions levels for each
boiler operating day by multiplying the
average hourly CO output concentration
measured by the CO CEMS times the
corresponding average hourly flue gas
flow rate and divided by the
corresponding average hourly useful
energy output from the affected facility.
The 24-hour average CO emission level
is determined by calculating the
arithmetic average of the hourly CO
emission levels computed for each
boiler operating day.
(3) You must evaluate the preceding
24-hour average CO emission level each
boiler operating day excluding periods
of affected facility startup, shutdown, or
malfunction. If the 24-hour average CO
emission level is greater than 1.4 lb/
MWh, you must initiate investigation of
the relevant equipment and control
systems within 24 hours of the first
discovery of the high emission incident
and, take the appropriate corrective
action as soon as practicable to adjust
control settings or repair equipment to
reduce the 24-hour average CO emission
level to 1.4 lb/MWh or less.
(4) You must record the CO
measurements and calculations
performed according to paragraph (u)(3)
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of this section and any corrective
actions taken. The record of corrective
action taken must include the date and
time during which the 24-hour average
CO emission level was greater than 1.4
lb/MWh, and the date, time, and
description of the corrective action.
(v) The owner or operator of an
affected facility using a CEMS
measuring PM emissions to meet
requirements of this subpart shall
install, certify, operate, and maintain
the CEMS as specified in paragraphs
(v)(1) through (v)(4) of this section.
*
*
*
*
*
(2) During each PM correlation testing
run of the CEMS required by
Performance Specification 11 in
appendix B of this part, PM and O2 (or
CO2) data shall be collected
concurrently (or within a 30- to 60minute period) by both the CEMS and
performance tests conducted using the
following test methods.
(i) For PM, Method 5 or 5B of
appendix A–3 of this part or Method 17
of appendix A–6 of this part shall be
used; and
(ii) After July 1, 2010 or after Method
202 of appendix M of part 51 has been
revised to minimize artifact
measurement and notice of that change
has been published in the Federal
Register, whichever is later, for
condensable PM emissions, Method 202
of appendix M of part 51 shall be used;
and
(iii) For O2 (or CO2), Method 3A or 3B
of appendix A–2 of this part, as
applicable shall be used.
*
*
*
*
*
(4) After July 1, 2011, within 90 days
after the date of completing each
performance evaluation required by
paragraph (v) of this section, the owner
or operator of the affected facility must
either submit the test data to EPA by
successfully entering the data
electronically into EPA’s WebFIRE data
base available at https://cfpub.epa.gov/
oarweb/index.cfm?action=fire.main or
mail a copy to: United States
Environmental Protection Agency;
Energy Strategies Group; 109 TW
Alexander DR; Mail Code: D243–01;
RTP, NC 27711.
(w) The owner or operator using a
SO2, NOX, CO2, and O2 CEMS to meet
the requirements of this subpart shall
install, certify, operate, and maintain
the CEMS as specified in paragraphs
(w)(1) through (w)(5) of this section.
(1) Except as provided for under
paragraphs (w)(2), (w)(3), and (w)(4) of
this section, each SO2, NOX, CO2, and
O2 CEMS required under paragraphs (b)
through (d) of this section shall be
installed, certified, and operated in
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accordance with the applicable
procedures in Performance
Specification 2 or 3 in appendix B to
this part or according to the procedures
in appendices A and B to part 75 of this
chapter. Daily calibration drift
assessments and quarterly accuracy
determinations shall be done in
accordance with Procedure 1 in
appendix F to this part, and a data
assessment report (DAR), prepared
according to section 7 of Procedure 1 in
appendix F to this part, shall be
submitted with each compliance report
required under § 60.51Da.
(2) As an alternative to meeting the
requirements of paragraph (w)(1) of this
section, an owner or operator may elect
to implement the following alternative
data accuracy assessment procedures.
For all required CO2 and O2 CEMS and
for SO2 and NOX CEMS with span
values greater than or equal to 100 ppm,
the daily calibration error test and
calibration adjustment procedures
described in sections 2.1.1 and 2.1.3 of
appendix B to part 75 of this chapter
may be followed instead of the CD
assessment procedures in Procedure 1,
section 4.1 of appendix F of this part. If
this option is selected, the data
validation and out-of-control provisions
in sections 2.1.4 and 2.1.5 of appendix
B to part 75 of this chapter shall be
followed instead of the excessive CD
and out-of-control criteria in Procedure
1, section 4.3 of appendix F to this part.
For the purposes of data validation
under this subpart, the excessive CD
and out-of-control criteria in Procedure
1, section 4.3 of appendix F to this part
shall apply to SO2 and NOX span values
less than 100 ppm;
*
*
*
*
*
12. Section 60.50Da is amended by
revising paragraphs (e)(1) and (f) to read
as follows:
■
§ 60.50Da Compliance determination
procedures and methods.
*
*
*
*
*
(e) * * *
(1) For Method 5 or 5B of appendix
A–3 of this part, Method 17 of appendix
A–6 of this part may be used at facilities
with or without wet FGD systems if the
stack temperature at the sampling
location does not exceed an average
temperature of 160 °C (320 °F). The
procedures of sections 8.1 and 11.1 of
Method 5B of appendix A–3 of this part
may be used in Method 17 of appendix
A–6 of this part only if it is used after
wet FGD systems. Method 17 of
appendix A–6 of this part shall not be
used after wet FGD systems if the
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effluent is saturated or laden with water
droplets.
*
*
*
*
*
(f) Electric utility combined cycle gas
turbines that are not designed to burn
fuels containing 50 percent (by heat
input) or more solid derived fuel not
meeting the definition of natural gas are
performance tested for PM, SO2, and
NOX using the procedures of Method 19
of appendix A–7 of this part. The SO2
and NOX emission rates calculations
from the gas turbine used in Method 19
of appendix A–7 of this part are
determined when the gas turbine is
performance tested under subpart GG of
this part. The potential uncontrolled PM
emission rate from a gas turbine is
defined as 17 ng/J (0.04 lb/MMBtu) heat
input.
*
*
*
*
*
■ 13. Section 60.51Da is amended by
revising paragraphs (b)(2) and (b)(3) to
read as follows:
§ 60.51Da
Reporting requirements.
*
*
*
*
*
(b) * * *
(2) The average SO2 and NOX
emission rates (ng/J, lb/MMBtu, or lb/
MWh) for each 30 successive boiler
operating days, ending with the last 30day period in the quarter; reasons for
non-compliance with the emission
standards; and, description of corrective
actions taken.
(3) For owners or operators of affected
facilities complying with the percent
reduction requirement, percent
reduction of the potential combustion
concentration of SO2 for each 30
successive boiler operating days, ending
with the last 30-day period in the
quarter; reasons for non-compliance
with the standard; and, description of
corrective actions taken.
*
*
*
*
*
■ 14. Section 60.52Da is revised to read
as follows:
§ 60.52Da
Recordkeeping requirements.
(a) The owner or operator of an
affected facility subject to the emissions
limitations in § 60.45Da shall provide
notifications in accordance with
§ 60.7(a) and shall maintain records of
all information needed to demonstrate
compliance including performance
tests, monitoring data, fuel analyses,
and calculations, consistent with the
requirements of § 60.7(f).
(b) The owner or operator of an
affected facility subject to the opacity
limits in § 60.42Da(b) that elects to
monitor emissions according to the
requirements in § 60.49Da(a)(3) shall
maintain records according to the
requirements specified in paragraphs
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(b)(1) through (3) of this section, as
applicable to the visible emissions
monitoring method used.
(1) For each performance test
conducted using Method 9 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(b)(1)(i) through (iii) of this section.
(i) Dates and time intervals of all
opacity observation periods;
(ii) Name, affiliation, and copy of
current visible emission reading
certification for each visible emission
observer participating in the
performance test; and
(iii) Copies of all visible emission
observer opacity field data sheets;
(2) For each performance test
conducted using Method 22 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(b)(2)(i) through (iv) of this section.
(i) Dates and time intervals of all
visible emissions observation periods;
(ii) Name and affiliation for each
visible emission observer participating
in the performance test;
(iii) Copies of all visible emission
observer opacity field data sheets; and
(iv) Documentation of any
adjustments made and the time the
adjustments were completed to the
affected facility operation by the owner
or operator to demonstrate compliance
with the applicable monitoring
requirements.
(3) For each digital opacity
compliance system, the owner or
operator shall maintain records and
submit reports according to the
requirements specified in the sitespecific monitoring plan approved by
the Administrator.
Subpart Db—[Amended]
15. Section 60.40b is amended by
revising the first sentence of paragraph
(i) to read as follows:
■
§ 60.40b Applicability and delegation of
authority.
sroberts on PROD1PC70 with RULES
*
*
*
*
*
(i) Heat recovery steam generators that
are associated with combined cycle gas
turbines and that meet the applicability
requirements of subpart KKKK of this
part are not subject to this subpart.
* * *
*
*
*
*
*
■ 16. Section 60.41b is amended by
revising the definitions of ‘‘Coal,’’
‘‘Distillate oil,’’ ‘‘Gaseous fuel,’’ ‘‘Gross
output,’’ ‘‘Natural gas,’’ ‘‘Potential sulfur
dioxide emission rate,’’ ‘‘Steam
generating unit,’’ and ‘‘Very low sulfur
oil’’ to read as follows:
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§ 60.41b
Definitions.
*
*
*
*
*
Coal means all solid fuels classified as
anthracite, bituminous, subbituminous,
or lignite by the American Society of
Testing and Materials in ASTM D388
(incorporated by reference, see § 60.17),
coal refuse, and petroleum coke. Coalderived synthetic fuels, including but
not limited to solvent refined coal,
gasified coal not meeting the definition
of natural gas, coal-oil mixtures, coke
oven gas, and coal-water mixtures, are
also included in this definition for the
purposes of this subpart.
*
*
*
*
*
Distillate oil means fuel oils that
contain 0.05 weight percent nitrogen or
less and comply with the specifications
for fuel oil numbers 1 and 2, as defined
by the American Society of Testing and
Materials in ASTM D396 (incorporated
by reference, see § 60.17) or diesel fuel
oil numbers 1 and 2, as defined by the
American Society for Testing and
Materials in ASTM D975 (incorporated
by reference, see § 60.17).
*
*
*
*
*
Gaseous fuel means any fuel that is a
gas at ISO conditions. This includes, but
is not limited to, natural gas and
gasified coal (including coke oven gas).
Gross output means the gross useful
work performed by the steam generated.
For units generating only electricity, the
gross useful work performed is the gross
electrical output from the turbine/
generator set. For cogeneration units,
the gross useful work performed is the
gross electrical or mechanical output
plus 75 percent of the useful thermal
output measured relative to ISO
conditions that is not used to generate
additional electrical or mechanical
output or to enhance the performance of
the unit (i.e., steam delivered to an
industrial process).
*
*
*
*
*
Natural gas means:
(1) A naturally occurring mixture of
hydrocarbon and nonhydrocarbon gases
found in geologic formations beneath
the earth’s surface, of which the
principal constituent is methane; or
(2) Liquefied petroleum gas, as
defined by the American Society for
Testing and Materials in ASTM D1835
(incorporated by reference, see § 60.17);
or
(3) A mixture of hydrocarbons that
maintains a gaseous state at ISO
conditions. Additionally, natural gas
must either be composed of at least 70
percent methane by volume or have a
gross calorific value between 34 and 43
megajoules (MJ) per dry standard cubic
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meter (910 and 1,150 Btu per dry
standard cubic foot).
*
*
*
*
*
Potential sulfur dioxide emission rate
means the theoretical SO2 emissions
(nanograms per joule (ng/J) or lb/
MMBtu heat input) that would result
from combusting fuel in an uncleaned
state and without using emission
control systems. For gasified coal or oil
that is desulfurized prior to combustion,
the Potential sulfur dioxide emission
rate is the theoretical SO2 emissions
(ng/J or lb/MMBtu heat input) that
would result from combusting fuel in a
cleaned state without using any post
combustion emission control systems.
*
*
*
*
*
Steam generating unit means a device
that combusts any fuel or byproduct/
waste and produces steam or heats
water or heats any heat transfer
medium. This term includes any
municipal-type solid waste incinerator
with a heat recovery steam generating
unit or any steam generating unit that
combusts fuel and is part of a
cogeneration system or a combined
cycle system. This term does not
include process heaters as they are
defined in this subpart.
*
*
*
*
*
Very low sulfur oil means for units
constructed, reconstructed, or modified
on or before February 28, 2005, oil that
contains no more than 0.5 weight
percent sulfur or that, when combusted
without SO2 emission control, has a SO2
emission rate equal to or less than 215
ng/J (0.5 lb/MMBtu) heat input. For
units constructed, reconstructed, or
modified after February 28, 2005 and
not located in a noncontinental area,
very low sulfur oil means oil that
contains no more than 0.30 weight
percent sulfur or that, when combusted
without SO2 emission control, has a SO2
emission rate equal to or less than 140
ng/J (0.32 lb/MMBtu) heat input. For
units constructed, reconstructed, or
modified after February 28, 2005 and
located in a noncontinental area, very
low sulfur oil means oil that contains no
more than 0.5 weight percent sulfur or
that, when combusted without SO2
emission control, has a SO2 emission
rate equal to or less than 215 ng/J (0.50
lb/MMBtu) heat input.
■ 17. Section 60.42b is amended to read
as follows:
■ a. By revising paragraph (a);
■ b. By revising paragraph (b);
■ c. By revising paragraph (c);
■ d. By revising paragraph (d)
introductory text; and
■ e. By revising paragraphs (k)(1), (k)(2),
and (k)(3).
E:\FR\FM\28JAR2.SGM
28JAR2
Standard for sulfur dioxide (SO2).
(a) Except as provided in paragraphs
(b), (c), (d), or (j) of this section, on and
after the date on which the performance
test is completed or required to be
completed under § 60.8, whichever
comes first, no owner or operator of an
affected facility that commenced
construction, reconstruction, or
modification on or before February 28,
2005, that combusts coal or oil shall
cause to be discharged into the
atmosphere any gases that contain SO2
in excess of 87 ng/J (0.20 lb/MMBtu) or
10 percent (0.10) of the potential SO2
emission rate (90 percent reduction) and
the emission limit determined according
to the following formula:
Es =
( K a Ha + K b Hb )
( Ha + Hb )
sroberts on PROD1PC70 with RULES
Where:
Es = SO2 emission limit, in ng/J or lb/MMBtu
heat input;
Ka = 520 ng/J (or 1.2 lb/MMBtu);
Kb = 340 ng/J (or 0.80 lb/MMBtu);
Ha = Heat input from the combustion of coal,
in J (MMBtu); and
Hb = Heat input from the combustion of oil,
in J (MMBtu).
For facilities complying with the
percent reduction standard, only the
heat input supplied to the affected
facility from the combustion of coal and
oil is counted in this paragraph. No
credit is provided for the heat input to
the affected facility from the combustion
of natural gas, wood, municipal-type
solid waste, or other fuels or heat
derived from exhaust gases from other
sources, such as gas turbines, internal
combustion engines, kilns, etc.
(b) On and after the date on which the
performance test is completed or
required to be completed under § 60.8,
whichever date comes first, no owner or
operator of an affected facility that
commenced construction,
reconstruction, or modification on or
before February 28, 2005, that combusts
coal refuse alone in a fluidized bed
combustion steam generating unit shall
cause to be discharged into the
atmosphere any gases that contain SO2
in excess of 87 ng/J (0.20 lb/MMBtu) or
20 percent (0.20) of the potential SO2
emission rate (80 percent reduction) and
520 ng/J (1.2 lb/MMBtu) heat input. If
coal or oil is fired with coal refuse, the
affected facility is subject to paragraph
(a) or (d) of this section, as applicable.
For facilities complying with the
percent reduction standard, only the
heat input supplied to the affected
facility from the combustion of coal and
oil is counted in this paragraph. No
credit is provided for the heat input to
the affected facility from the combustion
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of natural gas, wood, municipal-type
solid waste, or other fuels or heat
derived from exhaust gases from other
sources, such as gas turbines, internal
combustion engines, kilns, etc.
(c) On and after the date on which the
performance test is completed or is
required to be completed under § 60.8,
whichever comes first, no owner or
operator of an affected facility that
combusts coal or oil, either alone or in
combination with any other fuel, and
that uses an emerging technology for the
control of SO2 emissions, shall cause to
be discharged into the atmosphere any
gases that contain SO2 in excess of 50
percent of the potential SO2 emission
rate (50 percent reduction) and that
contain SO2 in excess of the emission
limit determined according to the
following formula:
Es =
( K c Hc + K d Hd )
( Hc + Hd )
Where:
Es = SO2 emission limit, in ng/J or lb/MM
Btu heat input;
Kc = 260 ng/J (or 0.60 lb/MMBtu);
Kd = 170 ng/J (or 0.40 lb/MMBtu);
Hc = Heat input from the combustion of coal,
in J (MMBtu); and
Hd = Heat input from the combustion of oil,
in J (MMBtu).
For facilities complying with the
percent reduction standard, only the
heat input supplied to the affected
facility from the combustion of coal and
oil is counted in this paragraph. No
credit is provided for the heat input to
the affected facility from the combustion
of natural gas, wood, municipal-type
solid waste, or other fuels, or from the
heat input derived from exhaust gases
from other sources, such as gas turbines,
internal combustion engines, kilns, etc.
(d) On and after the date on which the
performance test is completed or
required to be completed under § 60.8,
whichever comes first, no owner or
operator of an affected facility that
commenced construction,
reconstruction, or modification on or
before February 28, 2005 and listed in
paragraphs (d)(1), (2), (3), or (4) of this
section shall cause to be discharged into
the atmosphere any gases that contain
SO2 in excess of 520 ng/J (1.2 lb/
MMBtu) heat input if the affected
facility combusts coal, or 215 ng/J (0.5
lb/MMBtu) heat input if the affected
facility combusts oil other than very low
sulfur oil. Percent reduction
requirements are not applicable to
affected facilities under paragraphs
(d)(1), (2), (3) or (4) of this section. For
facilities complying with paragraphs
(d)(1), (2), or (3) of this section, only the
PO 00000
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Fmt 4701
Sfmt 4700
heat input supplied to the affected
facility from the combustion of coal and
oil is counted in this paragraph. No
credit is provided for the heat input to
the affected facility from the combustion
of natural gas, wood, municipal-type
solid waste, or other fuels or heat
derived from exhaust gases from other
sources, such as gas turbines, internal
combustion engines, kilns, etc.
*
*
*
*
*
(k)(1) Except as provided in
paragraphs (k)(2), (k)(3), and (k)(4) of
this section, on and after the date on
which the initial performance test is
completed or is required to be
completed under § 60.8, whichever date
comes first, no owner or operator of an
affected facility that commences
construction, reconstruction, or
modification after February 28, 2005,
and that combusts coal, oil, natural gas,
a mixture of these fuels, or a mixture of
these fuels with any other fuels shall
cause to be discharged into the
atmosphere any gases that contain SO2
in excess of 87 ng/J (0.20 lb/MMBtu)
heat input or 8 percent (0.08) of the
potential SO2 emission rate (92 percent
reduction) and 520 ng/J (1.2 lb/MMBtu)
heat input. For facilities complying with
the percent reduction standard and
paragraph (k)(3) of this section, only the
heat input supplied to the affected
facility from the combustion of coal and
oil is counted in paragraph (k) of this
section. No credit is provided for the
heat input to the affected facility from
the combustion of natural gas, wood,
municipal-type solid waste, or other
fuels or heat derived from exhaust gases
from other sources, such as gas turbines,
internal combustion engines, kilns, etc.
(2) Units firing only very low sulfur
oil, gaseous fuel, a mixture of these
fuels, or a mixture of these fuels with
any other fuels with a potential SO2
emission rate of 140 ng/J (0.32 lb/
MMBtu) heat input or less are exempt
from the SO2 emissions limit in
paragraph (k)(1) of this section.
(3) Units that are located in a
noncontinental area and that combust
coal, oil, or natural gas shall not
discharge any gases that contain SO2 in
excess of 520 ng/J (1.2 lb/MMBtu) heat
input if the affected facility combusts
coal, or 215 ng/J (0.50 lb/MMBtu) heat
input if the affected facility combusts oil
or natural gas.
*
*
*
*
*
■ 18. Section 60.43b is amended to read
as follows:
■ a. By revising paragraph (f);
■ b. By revising paragraph (g); and
■ c. By revising paragraphs (h)(1) and
(h)(5) and adding paragraph (h)(6).
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§ 60.42b
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§ 60.43b
(PM).
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Standard for particulate matter
sroberts on PROD1PC70 with RULES
*
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*
*
*
(f) On and after the date on which the
initial performance test is completed or
is required to be completed under
§ 60.8, whichever date comes first, no
owner or operator of an affected facility
that can combust coal, oil, wood, or
mixtures of these fuels with any other
fuels shall cause to be discharged into
the atmosphere any gases that exhibit
greater than 20 percent opacity (6minute average), except for one 6minute period per hour of not more than
27 percent opacity. Owners and
operators of an affected facility that
elect to install, calibrate, maintain, and
operate a continuous emissions
monitoring system (CEMS) for
measuring PM emissions according to
the requirements of this subpart and are
subject to a federally enforceable PM
limit of 0.030 lb/MMBtu or less are
exempt from the opacity standard
specified in this paragraph.
(g) The PM and opacity standards
apply at all times, except during periods
of startup, shutdown, or malfunction.
(h)(1) Except as provided in
paragraphs (h)(2), (h)(3), (h)(4), (h)(5),
and (h)(6) of this section, on and after
the date on which the initial
performance test is completed or is
required to be completed under § 60.8,
whichever date comes first, no owner or
operator of an affected facility that
commenced construction,
reconstruction, or modification after
February 28, 2005, and that combusts
coal, oil, wood, a mixture of these fuels,
or a mixture of these fuels with any
other fuels shall cause to be discharged
into the atmosphere from that affected
facility any gases that contain PM in
excess of 13 ng/J (0.030 lb/MMBtu) heat
input,
*
*
*
*
*
(5) On and after the date on which the
initial performance test is completed or
is required to be completed under
§ 60.8, whichever date comes first, an
owner or operator of an affected facility
not located in a noncontinental area that
commences construction,
reconstruction, or modification after
February 28, 2005, and that combusts
only oil that contains no more than 0.30
weight percent sulfur, coke oven gas, a
mixture of these fuels, or either fuel (or
a mixture of these fuels) in combination
with other fuels not subject to a PM
standard in § 60.43b and not using a
post-combustion technology (except a
wet scrubber) to reduce SO2 or PM
emissions is not subject to the PM limits
in (h)(1) of this section.
(6) On and after the date on which the
initial performance test is completed or
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Jkt 217001
is required to be completed under
§ 60.8, whichever date comes first, an
owner or operator of an affected facility
located in a noncontinental area that
commences construction,
reconstruction, or modification after
February 28, 2005, and that combusts
only oil that contains no more than 0.5
weight percent sulfur, coke oven gas, a
mixture of these fuels, or either fuel (or
a mixture of these fuels) in combination
with other fuels not subject to a PM
standard in § 60.43b and not using a
post-combustion technology (except a
wet scrubber) to reduce SO2 or PM
emissions is not subject to the PM limits
in (h)(1) of this section.
■ 19. Section 60.44b is amended by
revising paragraph (l)(1) to read as
follows:
§ 60.44b
(NOX).
Standard for nitrogen oxides
*
*
*
*
*
(l) * * *
(1) If the affected facility combusts
coal, oil, natural gas, a mixture of these
fuels, or a mixture of these fuels with
any other fuels: A limit of 86 ng/J (0.20
lb/MMBtu) heat input unless the
affected facility has an annual capacity
factor for coal, oil, and natural gas of 10
percent (0.10) or less and is subject to
a federally enforceable requirement that
limits operation of the facility to an
annual capacity factor of 10 percent
(0.10) or less for coal, oil, and natural
gas; or
*
*
*
*
*
■ 20. Section 60.45b is amended to read
as follows:
■ a. By revising paragraph (a);
■ b. By revising paragraphs (c)(2)(i),
(c)(4) introductory text, and (c)(5);
■ c. By revising paragraph (d)
introductory text;
■ d. By revising paragraph (j); and
■ e. By revising paragraph (k).
§ 60.45b Compliance and performance test
methods and procedures for sulfur dioxide.
(a) The SO2 emission standards in
§ 60.42b apply at all times. Facilities
burning coke oven gas alone or in
combination with any other gaseous
fuels or distillate oil are allowed to
exceed the limit 30 operating days per
calendar year for SO2 control system
maintenance.
*
*
*
*
*
(c) * * *
(2) * * *
(i) The procedures in Method 19 of
appendix A–7 of this part are used to
determine the hourly SO2 emission rate
(Eho) and the 30-day average emission
rate (Eao). The hourly averages used to
compute the 30-day averages are
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obtained from the CEMS of § 60.47b(a)
or (b).
*
*
*
*
*
(4) The owner or operator of an
affected facility subject to paragraph
(c)(3) of this section does not have to
measure parameters Ew or Xk if the
owner or operator elects to assume that
Xk= 1.0. Owners or operators of affected
facilities who assume Xk = 1.0 shall:
*
*
*
*
*
(5) The owner or operator of an
affected facility that qualifies under the
provisions of § 60.42b(d) does not have
to measure parameters Ew or Xk in
paragraph (c)(3) of this section if the
owner or operator of the affected facility
elects to measure SO2 emission rates of
the coal or oil following the fuel
sampling and analysis procedures in
Method 19 of appendix A–7 of this part.
(d) Except as provided in paragraph (j)
of this section, the owner or operator of
an affected facility that combusts only
very low sulfur oil, natural gas, or a
mixture of these fuels, has an annual
capacity factor for oil of 10 percent
(0.10) or less, and is subject to a
federally enforceable requirement
limiting operation of the affected facility
to an annual capacity factor for oil of 10
percent (0.10) or less shall:
*
*
*
*
*
(j) The owner or operator of an
affected facility that only combusts very
low sulfur oil, natural gas, or a mixture
of these fuels with any other fuels not
subject to an SO2 standard is not subject
to the compliance and performance
testing requirements of this section if
the owner or operator obtains fuel
receipts as described in § 60.49b(r).
(k) The owner or operator of an
affected facility seeking to demonstrate
compliance in §§ 60.42b(d)(4), 60.42b(j),
60.42b(k)(2), and 60.42b(k)(3) (when not
burning coal) shall follow the applicable
procedures in § 60.49b(r).
■ 21. Section 60.46b is amended to read
as follows:
■ a. By revising paragraphs (d)(1) and
(d)(2)(ii);
■ b. By revising paragraphs (e)(2) and
(e)(4);
■ c. By revising paragraph (g);
■ d. By revising paragraph (i); and
■ e. By revising paragraphs (j)
introductory text and (j)(11) and adding
paragraph (j)(14).
§ 60.46b Compliance and performance test
methods and procedures for particulate
matter and nitrogen oxides.
*
*
*
*
*
(d) * * *
(1) Method 3A or 3B of appendix A–
2 of this part is used for gas analysis
when applying Method 5 of appendix
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A–3 of this part or Method 17 of
appendix A–6 of this part.
(2) * * *
(ii) Method 17 of appendix A–6 of this
part may be used at facilities with or
without wet scrubber systems provided
the stack gas temperature does not
exceed a temperature of 160 °C (320 °F).
The procedures of sections 8.1 and 11.1
of Method 5B of appendix A–3 of this
part may be used in Method 17 of
appendix A–6 of this part only if it is
used after a wet FGD system. Do not use
Method 17 of appendix A–6 of this part
after wet FGD systems if the effluent is
saturated or laden with water droplets.
*
*
*
*
*
(e) * * *
(2) Following the date on which the
initial performance test is completed or
is required to be completed in § 60.8,
whichever date comes first, the owner
or operator of an affected facility which
combusts coal (except as specified
under § 60.46b(e)(4)) or which combusts
residual oil having a nitrogen content
greater than 0.30 weight percent shall
determine compliance with the NOX
emission standards in § 60.44b on a
continuous basis through the use of a
30-day rolling average emission rate. A
new 30-day rolling average emission
rate is calculated for each steam
generating unit operating day as the
average of all of the hourly NOX
emission data for the preceding 30
steam generating unit operating days.
*
*
*
*
*
(4) Following the date on which the
initial performance test is completed or
required to be completed under § 60.8,
whichever date comes first, the owner
or operator of an affected facility that
has a heat input capacity of 73 MW (250
MMBtu/hr) or less and that combusts
natural gas, distillate oil, gasified coal,
or residual oil having a nitrogen content
of 0.30 weight percent or less shall upon
request determine compliance with the
NOX standards in § 60.44b through the
use of a 30-day performance test. During
periods when performance tests are not
requested, NOX emissions data collected
pursuant to § 60.48b(g)(1) or
§ 60.48b(g)(2) are used to calculate a 30day rolling average emission rate on a
daily basis and used to prepare excess
emission reports, but will not be used to
determine compliance with the NOX
emission standards. A new 30-day
rolling average emission rate is
calculated each steam generating unit
operating day as the average of all of the
hourly NOX emission data for the
preceding 30 steam generating unit
operating days.
*
*
*
*
*
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(g) The owner or operator of an
affected facility described in § 60.44b(j)
or § 60.44b(k) shall demonstrate the
maximum heat input capacity of the
steam generating unit by operating the
facility at maximum capacity for 24
hours. The owner or operator of an
affected facility shall determine the
maximum heat input capacity using the
heat loss method or the heat input
method described in sections 5 and 7.3
of the ASME Power Test Codes 4.1
(incorporated by reference, see § 60.17).
This demonstration of maximum heat
input capacity shall be made during the
initial performance test for affected
facilities that meet the criteria of
§ 60.44b(j). It shall be made within 60
days after achieving the maximum
production rate at which the affected
facility will be operated, but not later
than 180 days after initial start-up of
each facility, for affected facilities
meeting the criteria of § 60.44b(k).
Subsequent demonstrations may be
required by the Administrator at any
other time. If this demonstration
indicates that the maximum heat input
capacity of the affected facility is less
than that stated by the manufacturer of
the affected facility, the maximum heat
input capacity determined during this
demonstration shall be used to
determine the capacity utilization rate
for the affected facility. Otherwise, the
maximum heat input capacity provided
by the manufacturer is used.
*
*
*
*
*
(i) The owner or operator of an
affected facility seeking to demonstrate
compliance with the PM limit in
paragraphs § 60.43b(a)(4) or
§ 60.43b(h)(5) shall follow the
applicable procedures in § 60.49b(r).
(j) In place of PM testing with Method
5 or 5B of appendix A–3 of this part, or
Method 17 of appendix A–6 of this part,
an owner or operator may elect to
install, calibrate, maintain, and operate
a CEMS for monitoring PM emissions
discharged to the atmosphere and
record the output of the system. The
owner or operator of an affected facility
who elects to continuously monitor PM
emissions instead of conducting
performance testing using Method 5 or
5B of appendix A–3 of this part or
Method 17 of appendix A–6 of this part
shall comply with the requirements
specified in paragraphs (j)(1) through
(j)(14) of this section.
*
*
*
*
*
(11) During the correlation testing
runs of the CEMS required by
Performance Specification 11 in
appendix B of this part, PM and O2 (or
CO2) data shall be collected
concurrently (or within a 30-to 60-
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5087
minute period) by both the continuous
emission monitors and performance
tests conducted using the following test
methods.
(i) For PM, Method 5 or 5B of
appendix A–3 of this part or Method 17
of appendix A–6 of this part shall be
used; and
(ii) After July 1, 2010 or after Method
202 of appendix M of part 51 has been
revised to minimize artifact
measurement and notice of that change
has been published in the Federal
Register, whichever is later, for
condensable PM emissions, Method 202
of appendix M of part 51 shall be used;
and
(iii) For O2 (or CO2), Method 3A or 3B
of appendix A–2 of this part, as
applicable shall be used.
*
*
*
*
*
(14) After July 1, 2011, within 90 days
after completing a correlation testing
run, the owner or operator of an affected
facility shall either successfully enter
the test data into EPA’s WebFIRE data
base located at https://cfpub.epa.gov/
oarweb/index.cfm?action=fire.main or
mail a copy to: United States
Environmental Protection Agency;
Energy Strategies Group; 109 TW
Alexander DR; Mail Code: D243–01;
RTP, NC 27711.
*
*
*
*
*
■ 22. Section 60.47b is amended by
revising the first sentence of paragraph
(a) introductory text and the first
sentence of paragraph (e)(4)(i) to read as
follows:
§ 60.47b
dioxide.
Emission monitoring for sulfur
(a) Except as provided in paragraphs
(b) and (f) of this section, the owner or
operator of an affected facility subject to
the SO2 standards in § 60.42b shall
install, calibrate, maintain, and operate
CEMS for measuring SO2 concentrations
and either O2 or CO2 concentrations and
shall record the output of the systems.
* * *
*
*
*
*
*
(e) * * *
(4) * * *
(i) For all required CO2 and O2
monitors and for SO2 and NOX monitors
with span values greater than or equal
to 100 ppm, the daily calibration error
test and calibration adjustment
procedures described in sections 2.1.1
and 2.1.3 of appendix B to part 75 of
this chapter may be followed instead of
the CD assessment procedures in
Procedure 1, section 4.1 of appendix F
to this part. * * *
*
*
*
*
*
■ 23. Section 60.48b is amended to read
as follows:
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a. By revising paragraph (a);
b. By revising paragraph (e)(1);
■ c. By revising paragraph (g)
introductory text;
■ d. By revising paragraph (h);
■ e. By revising paragraphs (j)
introductory text, the last sentence of
(j)(4) introductory text, (j)(4)(i)(C), (j)(5)
and adding (j)(6); and
■ f. By revising the first sentence of
paragraph (k).
■
■
sroberts on PROD1PC70 with RULES
§ 60.48b Emission monitoring for
particulate matter and nitrogen oxides.
(a) Except as provided in paragraph (j)
of this section, the owner or operator of
an affected facility subject to the opacity
standard under § 60.43b shall install,
calibrate, maintain, and operate a
continuous opacity monitoring systems
(COMS) for measuring the opacity of
emissions discharged to the atmosphere
and record the output of the system. The
owner or operator of an affected facility
subject to an opacity standard under
§ 60.43b and meeting the conditions
under paragraphs (j)(1), (2), (3), (4), or
(5) of this section who elects not to
install a COMS shall conduct a
performance test using Method 9 of
appendix A–4 of this part and the
procedures in § 60.11 to demonstrate
compliance with the applicable limit in
§ 60.43b and shall comply with either
paragraphs (a)(1), (a)(2), or (a)(3) of this
section. If during the initial 60 minutes
of observation all 6-minute averages are
less than 10 percent and all individual
15-second observations are less than or
equal to 20 percent, the observation
period may be reduced from 3 hours to
60 minutes.
(1) Except as provided in paragraph
(a)(2) and (a)(3) of this section, the
owner or operator shall conduct
subsequent Method 9 of appendix A–4
of this part performance tests using the
procedures in paragraph (a) of this
section according to the applicable
schedule in paragraphs (a)(1)(i) through
(a)(1)(iv) of this section, as determined
by the most recent Method 9 of
appendix A–4 of this part performance
test results.
(i) If no visible emissions are
observed, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 12
calendar months from the date that the
most recent performance test was
conducted;
(ii) If visible emissions are observed
but the maximum 6-minute average
opacity is less than or equal to 5
percent, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 6
calendar months from the date that the
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18:08 Jan 27, 2009
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most recent performance test was
conducted;
(iii) If the maximum 6-minute average
opacity is greater than 5 percent but less
than or equal to 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 3 calendar months
from the date that the most recent
performance test was conducted; or
(iv) If the maximum 6-minute average
opacity is greater than 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 30 calendar days from
the date that the most recent
performance test was conducted.
(2) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 of this part performance
tests, elect to perform subsequent
monitoring using Method 22 of
appendix A–7 of this part according to
the procedures specified in paragraphs
(a)(2)(i) and (ii) of this section.
(i) The owner or operator shall
conduct 10 minute observations (during
normal operation) each operating day
the affected facility fires fuel for which
an opacity standard is applicable using
Method 22 of appendix A–7 of this part
and demonstrate that the sum of the
occurrences of any visible emissions is
not in excess of 5 percent of the
observation period (i.e., 30 seconds per
10 minute period). If the sum of the
occurrence of any visible emissions is
greater than 30 seconds during the
initial 10 minute observation,
immediately conduct a 30 minute
observation. If the sum of the
occurrence of visible emissions is
greater than 5 percent of the observation
period (i.e., 90 seconds per 30 minute
period) the owner or operator shall
either document and adjust the
operation of the facility and
demonstrate within 24 hours that the
sum of the occurrence of visible
emissions is equal to or less than 5
percent during a 30 minute observation
(i.e., 90 seconds) or conduct a new
Method 9 of appendix A–4 of this part
performance test using the procedures
in paragraph (a) of this section within
30 calendar days according to the
requirements in § 60.46d(d)(7).
(ii) If no visible emissions are
observed for 30 operating days during
which an opacity standard is applicable,
observations can be reduced to once
every 7 operating days during which an
opacity standard is applicable. If any
visible emissions are observed, daily
observations shall be resumed.
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(3) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 performance tests, elect
to perform subsequent monitoring using
a digital opacity compliance system
according to a site-specific monitoring
plan approved by the Administrator.
The observations shall be similar, but
not necessarily identical, to the
requirements in paragraph (a)(2) of this
section. For reference purposes in
preparing the monitoring plan, see
OAQPS ‘‘Determination of Visible
Emission Opacity from Stationary
Sources Using Computer-Based
Photographic Analysis Systems.’’ This
document is available from the U.S.
Environmental Protection Agency (U.S.
EPA); Office of Air Quality and
Planning Standards; Sector Policies and
Programs Division; Measurement Policy
Group (D243–02), Research Triangle
Park, NC 27711. This document is also
available on the Technology Transfer
Network (TTN) under Emission
Measurement Center Preliminary
Methods.
*
*
*
*
*
(e) * * *
(1) For affected facilities combusting
coal, wood or municipal-type solid
waste, the span value for a COMS shall
be between 60 and 80 percent.
*
*
*
*
*
(g) The owner or operator of an
affected facility that has a heat input
capacity of 73 MW (250 MMBtu/hr) or
less, and that has an annual capacity
factor for residual oil having a nitrogen
content of 0.30 weight percent or less,
natural gas, distillate oil, gasified coal,
or any mixture of these fuels, greater
than 10 percent (0.10) shall:
*
*
*
*
*
(h) The owner or operator of a duct
burner, as described in § 60.41b, that is
subject to the NOX standards in
§ 60.44b(a)(4), § 60.44b(e), or § 60.44b(l)
is not required to install or operate a
continuous emissions monitoring
system to measure NOX emissions.
*
*
*
*
*
(j) The owner or operator of an
affected facility that meets the
conditions in either paragraph (j)(1), (2),
(3), (4), (5), or (6) of this section is not
required to install or operate a COMS if:
*
*
*
*
*
(4) * * * Owners and operators of
affected facilities electing to comply
with this paragraph must demonstrate
compliance according to the procedures
specified in paragraphs (j)(4)(i) through
(iv) of this section; or
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(i) * * *
(C) At a minimum, valid 1-hour CO
emissions averages must be obtained for
at least 90 percent of the operating
hours on a 30-day rolling average basis.
The 1-hour averages are calculated
using the data points required in
§ 60.13(h)(2).
*
*
*
*
*
(5) The affected facility uses a bag
leak detection system to monitor the
performance of a fabric filter (baghouse)
according to the most recent
requirements in section § 60.48Da of
this part; or
(6) The affected facility burns only
gaseous fuels or fuel oils that contain
less than or equal to 0.30 weight percent
sulfur and operates according to a
written site-specific monitoring plan
approved by the permitting authority.
This monitoring plan must include
procedures and criteria for establishing
and monitoring specific parameters for
the affected facility indicative of
compliance with the opacity standard.
(k) Owners or operators complying
with the PM emission limit by using a
PM CEMS must calibrate, maintain,
operate, and record the output of the
system for PM emissions discharged to
the atmosphere as specified in
§ 60.46b(j). * * *
■ 24. Section 60.49b is amended to read
as follows:
■ a. By revising paragraphs (c)
introductory text and (c)(3);
■ b. By revising paragraph (d);
■ c. By revising paragraph (f);
■ d. By revising paragraph (h)(1) and
(h)(2)(i);
■ e. By revising paragraph (k)(2);
■ f. By revising paragraph (m)
introductory text; and
■ g. By revising paragraph (r)(1).
§ 60.49b Reporting and recordkeeping
requirements.
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*
*
*
*
*
(c) The owner or operator of each
affected facility subject to the NOX
standard in § 60.44b who seeks to
demonstrate compliance with those
standards through the monitoring of
steam generating unit operating
conditions in the provisions of
§ 60.48b(g)(2) shall submit to the
Administrator for approval a plan that
identifies the operating conditions to be
monitored in § 60.48b(g)(2) and the
records to be maintained in § 60.49b(g).
This plan shall be submitted to the
Administrator for approval within 360
days of the initial startup of the affected
facility. An affected facility burning
coke oven gas alone or in combination
with other gaseous fuels or distillate oil
shall submit this plan to the
Administrator for approval within 360
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18:08 Jan 27, 2009
Jkt 217001
days of the initial startup of the affected
facility or by November 30, 2009,
whichever date comes later. If the plan
is approved, the owner or operator shall
maintain records of predicted nitrogen
oxide emission rates and the monitored
operating conditions, including steam
generating unit load, identified in the
plan. The plan shall:
*
*
*
*
*
(3) Identify how these operating
conditions, including steam generating
unit load, will be monitored under
§ 60.48b(g) on an hourly basis by the
owner or operator during the period of
operation of the affected facility; the
quality assurance procedures or
practices that will be employed to
ensure that the data generated by
monitoring these operating conditions
will be representative and accurate; and
the type and format of the records of
these operating conditions, including
steam generating unit load, that will be
maintained by the owner or operator
under § 60.49b(g).
(d) Except as provided in paragraph
(d)(2) of this section, the owner or
operator of an affected facility shall
record and maintain records as specified
in paragraph (d)(1) of this section.
(1) The owner or operator of an
affected facility shall record and
maintain records of the amounts of each
fuel combusted during each day and
calculate the annual capacity factor
individually for coal, distillate oil,
residual oil, natural gas, wood, and
municipal-type solid waste for the
reporting period. The annual capacity
factor is determined on a 12-month
rolling average basis with a new annual
capacity factor calculated at the end of
each calendar month.
(2) As an alternative to meeting the
requirements of paragraph (d)(1) of this
section, the owner or operator of an
affected facility that is subject to a
federally enforceable permit restricting
fuel use to a single fuel such that the
facility is not required to continuously
monitor any emissions (excluding
opacity) or parameters indicative of
emissions may elect to record and
maintain records of the amount of each
fuel combusted during each calendar
month.
*
*
*
*
*
(f) For an affected facility subject to
the opacity standard in § 60.43b, the
owner or operator shall maintain
records of opacity. In addition, an
owner or operator that elects to monitor
emissions according to the requirements
in § 60.48b(a) shall maintain records
according to the requirements specified
in paragraphs (f)(1) through (3) of this
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5089
section, as applicable to the visible
emissions monitoring method used.
(1) For each performance test
conducted using Method 9 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(f)(1)(i) through (iii) of this section.
(i) Dates and time intervals of all
opacity observation periods;
(ii) Name, affiliation, and copy of
current visible emission reading
certification for each visible emission
observer participating in the
performance test; and
(iii) Copies of all visible emission
observer opacity field data sheets;
(2) For each performance test
conducted using Method 22 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(f)(2)(i) through (iv) of this section.
(i) Dates and time intervals of all
visible emissions observation periods;
(ii) Name and affiliation for each
visible emission observer participating
in the performance test;
(iii) Copies of all visible emission
observer opacity field data sheets; and
(iv) Documentation of any
adjustments made and the time the
adjustments were completed to the
affected facility operation by the owner
or operator to demonstrate compliance
with the applicable monitoring
requirements.
(3) For each digital opacity
compliance system, the owner or
operator shall maintain records and
submit reports according to the
requirements specified in the sitespecific monitoring plan approved by
the Administrator.
*
*
*
*
*
(h) * * *
(1) Any affected facility subject to the
opacity standards in § 60.43b(f) or to the
operating parameter monitoring
requirements in § 60.13(i)(1).
(2) * * *
(i) Combusts natural gas, distillate oil,
gasified coal, or residual oil with a
nitrogen content of 0.3 weight percent
or less; or
*
*
*
*
*
(k) * * *
(2) Each 30-day average SO2 emission
rate (ng/J or lb/MMBtu heat input)
measured during the reporting period,
ending with the last 30-day period;
reasons for noncompliance with the
emission standards; and a description of
corrective actions taken; For an
exceedance due to maintenance of the
SO2 control system covered in
paragraph 60.45b(a), the report shall
identify the days on which the
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maintenance was performed and a
description of the maintenance;
*
*
*
*
*
(m) For each affected facility subject
to the SO2 standards in § 60.42(b) for
which the minimum amount of data
required in § 60.47b(c) were not
obtained during the reporting period,
the following information is reported to
the Administrator in addition to that
required under paragraph (k) of this
section:
*
*
*
*
*
(r) * * *
(1) The owner or operator of an
affected facility who elects to
demonstrate that the affected facility
combusts only very low sulfur oil,
natural gas, wood, a mixture of these
fuels, or any of these fuels (or a mixture
of these fuels) in combination with
other fuels that are known to contain an
insignificant amount of sulfur in
§ 60.42b(j) or § 60.42b(k) shall obtain
and maintain at the affected facility fuel
receipts from the fuel supplier that
certify that the oil meets the definition
of distillate oil and gaseous fuel meets
the definition of natural gas as defined
in § 60.41b and the applicable sulfur
limit. For the purposes of this section,
the distillate oil need not meet the fuel
nitrogen content specification in the
definition of distillate oil. Reports shall
be submitted to the Administrator
certifying that only very low sulfur oil
meeting this definition, natural gas,
wood, and/or other fuels that are known
to contain insignificant amounts of
sulfur were combusted in the affected
facility during the reporting period; or
*
*
*
*
*
Subpart Dc—[Amended]
25. Section 60.40c is amended to read
as follows:
■ a. By revising paragraph (a);
■ b. By revising the first sentence of
paragraph (e);
■ c. By revising paragraph (f); and
■ d. By revising paragraph (g).
■
§ 60.40c Applicability and delegation of
authority.
(a) Except as provided in paragraphs
(d), (e), (f), and (g) of this section, the
affected facility to which this subpart
applies is each steam generating unit for
which construction, modification, or
reconstruction is commenced after June
9, 1989 and that has a maximum design
heat input capacity of 29 megawatts
(MW) (100 million British thermal units
per hour (MMBtu/hr)) or less, but
greater than or equal to 2.9 MW (10
MMBtu/hr).
*
*
*
*
*
(e) Heat recovery steam generators
that are associated with combined cycle
gas turbines and meet the applicability
requirements of subpart KKKK of this
part are not subject to this subpart.
* * *
(f) Any facility covered by subpart
AAAA of this part is not subject by this
subpart.
(g) Any facility covered by an EPA
approved State or Federal section
111(d)/129 plan implementing subpart
BBBB of this part is not subject by this
subpart.
■ 26. Section 60.41c is amended by
revising the definitions of ‘‘Coal,’’
‘‘Distillate oil,’’ ‘‘Natural gas,’’ and
‘‘Steam generating unit’’ to read as
follows:
§ 60.41c
Definitions.
*
*
*
*
*
Coal means all solid fuels classified as
anthracite, bituminous, subbituminous,
or lignite by the American Society of
Testing and Materials in ASTM D388
(incorporated by reference, see § 60.17),
coal refuse, and petroleum coke. Coalderived synthetic fuels derived from
coal for the purposes of creating useful
heat, including but not limited to
solvent refined coal, gasified coal not
meeting the definition of natural gas,
coal-oil mixtures, and coal-water
mixtures, are also included in this
definition for the purposes of this
subpart.
*
*
*
*
*
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Es =
Where:
Es = SO2 emission limit, expressed in ng/J or
lb/MMBtu heat input;
Ka = 520 ng/J (1.2 lb/MMBtu);
Kb = 260 ng/J (0.60 lb/MMBtu);
Kc = 215 ng/J (0.50 lb/MMBtu);
Ha = Heat input from the combustion of coal,
except coal combusted in an affected
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§ 60.42c
Standard for sulfur dioxide (SO2).
*
*
*
*
*
(e) * * *
(2) The emission limit determined
according to the following formula for
any affected facility that combusts coal,
oil, or coal and oil with any other fuel:
( K a Ha + K b Hb + K c Hc )
( Ha + Hb + Hc )
facility subject to paragraph (b)(2) of this
section, in Joules (J) [MMBtu];
Hb = Heat input from the combustion of coal
in an affected facility subject to
paragraph (b)(2) of this section, in J
(MMBtu); and
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Distillate oil means fuel oil that
complies with the specifications for fuel
oil numbers 1 or 2, as defined by the
American Society for Testing and
Materials in ASTM D396 (incorporated
by reference, see § 60.17) or diesel fuel
oil numbers 1 or 2, as defined by the
American Society for Testing and
Materials in ASTM D975 (incorporated
by reference, see § 60.17).
*
*
*
*
*
Natural gas means:
(1) A naturally occurring mixture of
hydrocarbon and nonhydrocarbon gases
found in geologic formations beneath
the earth’s surface, of which the
principal constituent is methane; or
(2) Liquefied petroleum (LP) gas, as
defined by the American Society for
Testing and Materials in ASTM D1835
(incorporated by reference, see § 60.17);
or
(3) A mixture of hydrocarbons that
maintains a gaseous state at ISO
conditions. Additionally, natural gas
must either be composed of at least 70
percent methane by volume or have a
gross calorific value between 34 and 43
megajoules (MJ) per dry standard cubic
meter (910 and 1,150 Btu per dry
standard cubic foot).
*
*
*
*
*
Steam generating unit means a device
that combusts any fuel and produces
steam or heats water or heats any heat
transfer medium. This term includes
any duct burner that combusts fuel and
is part of a combined cycle system. This
term does not include process heaters as
defined in this subpart.
*
*
*
*
*
■ 27. Section 60.42c is amended by
revising paragraphs (e)(2) and (j) to read
as follows:
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Hc = Heat input from the combustion of oil,
in J (MMBtu).
*
*
*
*
*
(j) For affected facilities located in
noncontinental areas and affected
facilities complying with the percent
reduction standard, only the heat input
supplied to the affected facility from the
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combustion of coal and oil is counted
under this section. No credit is provided
for the heat input to the affected facility
from wood or other fuels or for heat
derived from exhaust gases from other
sources, such as stationary gas turbines,
internal combustion engines, and kilns.
■ 28. Section 60.43c is amended by
revising paragraph (c) to read as follows:
§ 60.43c
(PM).
Standard for particulate matter
*
*
*
*
*
(c) On and after the date on which the
initial performance test is completed or
required to be completed under § 60.8,
whichever date comes first, no owner or
operator of an affected facility that can
combust coal, wood, or oil and has a
heat input capacity of 8.7 MW (30
MMBtu/hr) or greater shall cause to be
discharged into the atmosphere from
that affected facility any gases that
exhibit greater than 20 percent opacity
(6-minute average), except for one 6minute period per hour of not more than
27 percent opacity. Owners and
operators of an affected facility that
elect to install, calibrate, maintain, and
operate a continuous emissions
monitoring system (CEMS) for
measuring PM emissions according to
the requirements of this subpart and are
subject to a federally enforceable PM
limit of 0.030 lb/MMBtu or less are
exempt from the opacity standard
specified in this paragraph.
*
*
*
*
*
■ 29. Section 60.44c is amended by
revising paragraph (h) to read as
follows:
§ 60.44c Compliance and performance test
methods and procedures for sulfur dioxide.
*
*
*
*
(h) For affected facilities subject to
§ 60.42c(h)(1), (2), or (3) where the
owner or operator seeks to demonstrate
compliance with the SO2 standards
based on fuel supplier certification, the
performance test shall consist of the
certification from the fuel supplier, as
described in § 60.48c(f), as applicable.
*
*
*
*
*
■ 30. Section 60.45c is amended to read
as follows:
■ a. By revising paragraphs (a)(2) and
(a)(8);
■ b. By revising paragraphs (c)
introductory text, (c)(7) introductory
text, (c)(8), (c)(9), and (c)(11), and by
adding paragraph (c)(14).
sroberts on PROD1PC70 with RULES
*
§ 60.45c Compliance and performance test
methods and procedures for particulate
matter.
(a) * * *
(2) Method 3A or 3B of appendix A–
2 of this part shall be used for gas
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analysis when applying Method 5 or 5B
of appendix A–3 of this part or 17 of
appendix A–6 of this part.
*
*
*
*
*
(8) Method 9 of appendix A–4 of this
part shall be used for determining the
opacity of stack emissions.
*
*
*
*
*
(c) In place of PM testing with Method
5 or 5B of appendix A–3 of this part or
Method 17 of appendix A–6 of this part,
an owner or operator may elect to
install, calibrate, maintain, and operate
a CEMS for monitoring PM emissions
discharged to the atmosphere and
record the output of the system. The
owner or operator of an affected facility
who elects to continuously monitor PM
emissions instead of conducting
performance testing using Method 5 or
5B of appendix A–3 of this part or
Method 17 of appendix A–6 of this part
shall install, calibrate, maintain, and
operate a CEMS and shall comply with
the requirements specified in
paragraphs (c)(1) through (c)(14) of this
section.
*
*
*
*
*
(7) At a minimum, valid CEMS hourly
averages shall be obtained as specified
in paragraph (c)(7)(i) of this section for
75 percent of the total operating hours
per 30-day rolling average.
*
*
*
*
*
(8) The 1-hour arithmetic averages
required under paragraph (c)(7) of this
section shall be expressed in ng/J or lb/
MMBtu heat input and shall be used to
calculate the boiler operating day daily
arithmetic average emission
concentrations. The 1-hour arithmetic
averages shall be calculated using the
data points required under § 60.13(e)(2)
of subpart A of this part.
(9) All valid CEMS data shall be used
in calculating average emission
concentrations even if the minimum
CEMS data requirements of paragraph
(c)(7) of this section are not met.
*
*
*
*
*
(11) During the correlation testing
runs of the CEMS required by
Performance Specification 11 in
appendix B of this part, PM and O2 (or
CO2) data shall be collected
concurrently (or within a 30- to 60minute period) by both the continuous
emission monitors and performance
tests conducted using the following test
methods.
(i) For PM, Method 5 or 5B of
appendix A–3 of this part or Method 17
of appendix A–6 of this part shall be
used; and
(ii) After July 1, 2010 or after Method
202 of appendix M of part 51 has been
revised to minimize artifact
measurement and notice of that change
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5091
has been published in the Federal
Register, whichever is later, for
condensable PM emissions, Method 202
of appendix M of part 51 shall be used;
and
(iii) For O2 (or CO2), Method 3A or 3B
of appendix A–2 of this part, as
applicable shall be used.
*
*
*
*
*
(14) After July 1, 2011, within 90 days
after the date of completing each
performance evaluation required by
paragraph (c)(11) of this section, the
owner or operator of the affected facility
must either submit the test data to EPA
by successfully entering the data
electronically into EPA’s WebFIRE data
base available at https://cfpub.epa.gov/
oarweb/index.cfm?action=fire.main or
mail a copy to: United States
Environmental Protection Agency;
Energy Strategies Group; 109 TW
Alexander DR; Mail Code: D243–01;
RTP, NC 27711.
*
*
*
*
*
■ 31. Section 60.47c is amended to read
as follows:
■ a. By revising paragraph (a);
■ b. By revising paragraph (b);
■ c. By revising paragraph (c);
■ d. By revising paragraph (d);
■ e. By revising paragraphs (e)
introductory text and (e)(1)(iii);
■ f. By revising paragraph (f); and
■ g. By adding paragraph (g).
§ 60.47c Emission monitoring for
particulate matter.
(a) Except as provided in paragraphs
(c), (d), (e), (f), and (g) of this section,
the owner or operator of an affected
facility combusting coal, oil, or wood
that is subject to the opacity standards
under § 60.43c shall install, calibrate,
maintain, and operate a continuous
opacity monitoring system (COMS) for
measuring the opacity of the emissions
discharged to the atmosphere and
record the output of the system. The
owner or operator of an affected facility
subject to an opacity standard in
§ 60.43c(c) and that is not required to
install a COMS due to paragraphs (c),
(d), (e), or (f) of this section that elects
not to install a COMS shall conduct a
performance test using Method 9 of
appendix A–4 of this part and the
procedures in § 60.11 to demonstrate
compliance with the applicable limit in
§ 60.43c and shall comply with either
paragraphs (a)(1), (a)(2), or (a)(3) of this
section. If during the initial 60 minutes
of observation all 6-minute averages are
less than 10 percent and all individual
15-second observations are less than or
equal to 20 percent, the observation
period may be reduced from 3 hours to
60 minutes.
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Federal Register / Vol. 74, No. 17 / Wednesday, January 28, 2009 / Rules and Regulations
(1) Except as provided in paragraph
(a)(2) and (a)(3) of this section, the
owner or operator shall conduct
subsequent Method 9 of appendix A–4
of this part performance tests using the
procedures in paragraph (a) of this
section according to the applicable
schedule in paragraphs (a)(1)(i) through
(a)(1)(iv) of this section, as determined
by the most recent Method 9 of
appendix A–4 of this part performance
test results.
(i) If no visible emissions are
observed, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 12
calendar months from the date that the
most recent performance test was
conducted;
(ii) If visible emissions are observed
but the maximum 6-minute average
opacity is less than or equal to 5
percent, a subsequent Method 9 of
appendix A–4 of this part performance
test must be completed within 6
calendar months from the date that the
most recent performance test was
conducted;
(iii) If the maximum 6-minute average
opacity is greater than 5 percent but less
than or equal to 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 3 calendar months
from the date that the most recent
performance test was conducted; or
(iv) If the maximum 6-minute average
opacity is greater than 10 percent, a
subsequent Method 9 of appendix A–4
of this part performance test must be
completed within 30 calendar days from
the date that the most recent
performance test was conducted.
(2) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 of this part performance
tests, elect to perform subsequent
monitoring using Method 22 of
appendix A–7 of this part according to
the procedures specified in paragraphs
(a)(2)(i) and (ii) of this section.
(i) The owner or operator shall
conduct 10 minute observations (during
normal operation) each operating day
the affected facility fires fuel for which
an opacity standard is applicable using
Method 22 of appendix A–7 of this part
and demonstrate that the sum of the
occurrences of any visible emissions is
not in excess of 5 percent of the
observation period (i.e. , 30 seconds per
10 minute period). If the sum of the
occurrence of any visible emissions is
greater than 30 seconds during the
initial 10 minute observation,
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immediately conduct a 30 minute
observation. If the sum of the
occurrence of visible emissions is
greater than 5 percent of the observation
period (i.e. , 90 seconds per 30 minute
period) the owner or operator shall
either document and adjust the
operation of the facility and
demonstrate within 24 hours that the
sum of the occurrence of visible
emissions is equal to or less than 5
percent during a 30 minute observation
(i.e. , 90 seconds) or conduct a new
Method 9 of appendix A–4 of this part
performance test using the procedures
in paragraph (a) of this section within
30 calendar days according to the
requirements in § 60.45c(a)(8).
(ii) If no visible emissions are
observed for 30 operating days during
which an opacity standard is applicable,
observations can be reduced to once
every 7 operating days during which an
opacity standard is applicable. If any
visible emissions are observed, daily
observations shall be resumed.
(3) If the maximum 6-minute opacity
is less than 10 percent during the most
recent Method 9 of appendix A–4 of this
part performance test, the owner or
operator may, as an alternative to
performing subsequent Method 9 of
appendix A–4 performance tests, elect
to perform subsequent monitoring using
a digital opacity compliance system
according to a site-specific monitoring
plan approved by the Administrator.
The observations shall be similar, but
not necessarily identical, to the
requirements in paragraph (a)(2) of this
section. For reference purposes in
preparing the monitoring plan, see
OAQPS ‘‘Determination of Visible
Emission Opacity from Stationary
Sources Using Computer-Based
Photographic Analysis Systems.’’ This
document is available from the U.S.
Environmental Protection Agency (U.S.
EPA); Office of Air Quality and
Planning Standards; Sector Policies and
Programs Division; Measurement Policy
Group (D243–02), Research Triangle
Park, NC 27711. This document is also
available on the Technology Transfer
Network (TTN) under Emission
Measurement Center Preliminary
Methods.
(b) All COMS shall be operated in
accordance with the applicable
procedures under Performance
Specification 1 of appendix B of this
part. The span value of the opacity
COMS shall be between 60 and 80
percent.
(c) Owners and operators of an
affected facilities that burn only
distillate oil that contains no more than
0.5 weight percent sulfur and/or liquid
or gaseous fuels with potential sulfur
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Fmt 4701
Sfmt 4700
dioxide emission rates of 26 ng/J (0.060
lb/MMBtu) heat input or less and that
do not use a post-combustion
technology to reduce SO2 or PM
emissions and that are subject to an
opacity standard in § 60.43c(c) are not
required to operate a COMS if they
follow the applicable procedures in
§ 60.48c(f).
(d) Owners or operators complying
with the PM emission limit by using a
PM CEMS must calibrate, maintain,
operate, and record the output of the
system for PM emissions discharged to
the atmosphere as specified in
§ 60.45c(c). The CEMS specified in
paragraph § 60.45c(c) shall be operated
and data recorded during all periods of
operation of the affected facility except
for CEMS breakdowns and repairs. Data
is recorded during calibration checks,
and zero and span adjustments.
(e) Owners and operators of an
affected facility that is subject to an
opacity standard in § 60.43c(c) and that
does not use post-combustion
technology (except a wet scrubber) for
reducing PM, SO2, or carbon monoxide
(CO) emissions, burns only gaseous
fuels or fuel oils that contain less than
or equal to 0.5 weight percent sulfur,
and is operated such that emissions of
CO discharged to the atmosphere from
the affected facility are maintained at
levels less than or equal to 0.15 lb/
MMBtu on a boiler operating day
average basis is not required to operate
a COMS. Owners and operators of
affected facilities electing to comply
with this paragraph must demonstrate
compliance according to the procedures
specified in paragraphs (e)(1) through
(4) of this section; or
(1) * * *
(iii) At a minimum, valid 1-hour CO
emissions averages must be obtained for
at least 90 percent of the operating
hours on a 30-day rolling average basis.
The 1-hour averages are calculated
using the data points required in
§ 60.13(h)(2).
*
*
*
*
*
(f) Owners and operators of an
affected facility that is subject to an
opacity standard in § 60.43c(c) and that
uses a bag leak detection system to
monitor the performance of a fabric
filter (baghouse) according to the most
recent requirements in section § 60.48Da
of this part is not required to operate a
COMS.
(g) Owners and operators of an
affected facility that is subject to an
opacity standard in § 60.43c(c) and that
burns only gaseous fuels or fuel oils that
contain less than or equal to 0.5 weight
percent sulfur and operates according to
a written site-specific monitoring plan
E:\FR\FM\28JAR2.SGM
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Federal Register / Vol. 74, No. 17 / Wednesday, January 28, 2009 / Rules and Regulations
approved by the permitting authority is
not required to operate a COMS. This
monitoring plan must include
procedures and criteria for establishing
and monitoring specific parameters for
the affected facility indicative of
compliance with the opacity standard.
■ 32. Section 60.48c is amended to read
as follows:
■ a. By revising paragraph (c);
■ b. By revising paragraph (e)(11); and
■ c. By revising paragraphs (f)(1)(iii) and
(f)(4)(ii).
§ 60.48c Reporting and recordkeeping
requirements.
*
*
*
*
(c) In addition to the applicable
requirements in § 60.7, the owner or
operator of an affected facility subject to
the opacity limits in § 60.43c(c) shall
submit excess emission reports for any
excess emissions from the affected
facility that occur during the reporting
period and maintain records according
to the requirements specified in
paragraphs (c)(1) through (3) of this
section, as applicable to the visible
emissions monitoring method used.
(1) For each performance test
conducted using Method 9 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
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information specified in paragraphs
(c)(1)(i) through (iii) of this section.
(i) Dates and time intervals of all
opacity observation periods;
(ii) Name, affiliation, and copy of
current visible emission reading
certification for each visible emission
observer participating in the
performance test; and
(iii) Copies of all visible emission
observer opacity field data sheets;
(2) For each performance test
conducted using Method 22 of appendix
A–4 of this part, the owner or operator
shall keep the records including the
information specified in paragraphs
(c)(2)(i) through (iv) of this section.
(i) Dates and time intervals of all
visible emissions observation periods;
(ii) Name and affiliation for each
visible emission observer participating
in the performance test;
(iii) Copies of all visible emission
observer opacity field data sheets; and
(iv) Documentation of any
adjustments made and the time the
adjustments were completed to the
affected facility operation by the owner
or operator to demonstrate compliance
with the applicable monitoring
requirements.
(3) For each digital opacity
compliance system, the owner or
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5093
operator shall maintain records and
submit reports according to the
requirements specified in the sitespecific monitoring plan approved by
the Administrator
*
*
*
*
*
(e) * * *
(11) If fuel supplier certification is
used to demonstrate compliance,
records of fuel supplier certification as
described under paragraph (f)(1), (2), (3),
or (4) of this section, as applicable. In
addition to records of fuel supplier
certifications, the report shall include a
certified statement signed by the owner
or operator of the affected facility that
the records of fuel supplier
certifications submitted represent all of
the fuel combusted during the reporting
period.
(f) * * *
(1) * * *
(iii) The sulfur content or maximum
sulfur content of the oil.
*
*
*
*
*
(4) * * *
(ii) The potential sulfur emissions rate
or maximum potential sulfur emissions
rate of the fuel in ng/J heat input; and
*
*
*
*
*
[FR Doc. E9–523 Filed 1–27–09; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\28JAR2.SGM
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Agencies
[Federal Register Volume 74, Number 17 (Wednesday, January 28, 2009)]
[Rules and Regulations]
[Pages 5072-5093]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-523]
[[Page 5071]]
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Part III
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 60
Standards of Performance for Fossil-Fuel-Fired Steam Generators;
Standards of Performance for Industrial-Commercial-Institutional Steam
Generating Units; Final Rule
Federal Register / Vol. 74, No. 17 / Wednesday, January 28, 2009 /
Rules and Regulations
[[Page 5072]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 60
[EPA-HQ-OAR-2005-0031; FRL-8748-2]
RIN 2060-AO61
Standards of Performance for Fossil-Fuel-Fired Steam Generators
for Which Construction Is Commenced After August 17, 1971; Standards of
Performance for Electric Utility Steam Generating Units for Which
Construction Is Commenced After September 18, 1978; Standards of
Performance for Industrial-Commercial-Institutional Steam Generating
Units; and Standards of Performance for Small Industrial-Commercial-
Institutional Steam Generating Units
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is amending the new source performance standards (NSPS)
for electric utility steam generating units and industrial-commercial-
institutional steam generating units. These amendments to the
regulations are to add compliance alternatives for owners and operators
of certain affected sources, eliminate the opacity standard for
facilities with a particulate matter (PM) limit of 0.030 lb/million
British thermal units (MMBtu) or less that choose to voluntarily
install and use PM continuous emission monitors (CEMS) to demonstrate
compliance with that limit, and to correct technical and editorial
errors.
DATES: This final rule is effective on January 28, 2009. The
incorporation by reference of certain publications listed in this final
rule is approved by the Director of the Federal Register as of January
28, 2009.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-HQ-OAR-2005-0031. All documents in the docket are listed in the
Federal Docket Management System index at https://www.regulations.gov.
Although listed in the index, some information is not publicly
available, e.g. , confidential business information or other
information whose disclosure is restricted by statute. Certain other
material, such as copyrighted material, is not placed on the Internet
and will be publicly available only in hard copy form. Publicly
available docket materials are available either electronically through
https://www.regulations.gov or in hard copy at the EPA Docket Center,
Public Reading Room, EPA West, Room 3334, 1301 Constitution Ave., NW.,
Washington, DC. The Public Reading Room is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding legal holidays. The telephone
number for the Public Reading Room is (202) 566-1744, and the telephone
number for the Air Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Mr. Christian Fellner, Energy
Strategies Group, Sector Policies and Programs Division (D243-01), U.S.
EPA, Research Triangle Park, NC 27711, telephone number (919) 541-4003,
facsimile number (919) 541-5450, electronic mail (e-mail) address:
fellner.christian@epa.gov.
SUPPLEMENTARY INFORMATION: Outline. The information presented in this
preamble is organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document?
C. Judicial Review
II. Background Information
III. Final Amendments and Response to Public Comments
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. General Information
A. Does this action apply to me?
The regulated categories and entities potentially affected by this
final action include, but are not limited to, the following:
------------------------------------------------------------------------
Examples of potentially
Category NAICS Code\1\ regulated entities
------------------------------------------------------------------------
Industry....................... 221112 Fossil fuel-fired
electric utility steam
generating units.
Federal Government............. 22112 Fossil fuel-fired
electric utility steam
generating units owned
by the Federal
Government.
State/local/ tribal government. 22112 Fossil fuel-fired
electric utility steam
generating units owned
by municipalities.
921150 Fossil fuel-fired
electric steam
generating units in
Indian Country.
Any industrial, commercial, or 211 Extractors of crude
institutional facility using a petroleum and natural
steam generating unit as gas.
defined in 60.40b or 60.4c.
321 Manufacturers of lumber
and wood products.
322 Pulp and paper mills.
325 Chemical manufacturers.
324 Petroleum refiners and
manufacturers of coal
products.
316, 326, 339 Manufacturers of rubber
and miscellaneous
plastic products.
331 Steel works, blast
furnaces.
332 Electroplating,
plating, polishing,
anodizing, and
coloring.
336 Manufacturers of motor
vehicle parts and
accessories.
221 Electric, gas, and
sanitary services.
622 Health services.
611 Educational services.
------------------------------------------------------------------------
\1\ North American Industry Classification System (NAICS) code.
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
action. To determine whether your facility is regulated by this action,
you should examine the
[[Page 5073]]
applicability criteria in Sec. 60.40, Sec. 60.40a, Sec. 60.40b, or
Sec. 60.40c of 40 CFR part 60. If you have any questions regarding the
applicability of this action to a particular entity, consult either the
air permit authority for the entity or your EPA regional representative
as listed in Sec. 63.13 of subpart A (General Provisions) of title 40
of the Code of Federal Regulations.
B. Where can I get a copy of this document?
In addition to being available in the docket, an electronic copy of
this final action will also be available on the Worldwide Web (WWW)
through the Technology Transfer Network (TTN). Following signature, a
copy of this final action will be posted on the TTN's policy and
guidance page for newly proposed or promulgated rules at the following
address: https://www.epa.gov/ttn/oarpg/. The TTN provides information
and technology exchange in various areas of air pollution control.
C. Judicial Review
Under section 307(b)(1) of the Clean Air Act (CAA), judicial review
of these final rules is available only by filing a petition for review
in the U.S. Court of Appeals for the District of Columbia Circuit by
March 30, 2009. Under section 307(d)(7)(B) of the CAA, only an
objection to these final rules that was raised with reasonable
specificity during the period for public comment can be raised during
judicial review. Moreover, under section 307(b)(2) of the CAA, the
requirements established by these final rules may not be challenged
separately in any civil or criminal proceedings brought by EPA to
enforce these requirements.
II. Background Information
In response to petitions for reconsideration of the amendments to
the new source performance standards for steam generating units that
EPA promulgated on June 13, 2007 (72 FR 32710) filed by the Coke Oven
Environmental Task Force, EPA proposed revised amendments to address
issues for which the petitioners requested reconsideration (see docket
entry EPA-HQ-OAR-2005-0031-0276). EPA also proposed certain other
unrelated amendments it felt were appropriate. In sum, EPA proposed on
June 12, 2008 (73 FR 33642) to amend subparts D, Da, Db, and Dc of 40
CFR part 60 to clarify the intent for applying and implementing
specific rule requirements, provide additional compliance alternatives,
and to correct unintentional technical omissions and editorial errors.
A 45-day comment period (June 12, 2008 to July 28, 2008) was
provided to accept comments on the proposed rule. An opportunity for a
public hearing was provided to allow any interested persons to present
oral comments on the proposed rule. However, EPA did not receive a
request for a formal public hearing, so a public hearing was not held.
We received comments on the proposed amendments from 11 commenters
during the comment period.
III. Final Amendments and Response to Public Comments
We are amending subparts D, Da, Db, and Dc of 40 CFR part 60 to add
compliance alternatives for owners/operators of certain affected
sources, to eliminate the opacity standard for certain facilities
voluntarily using PM CEMS, and to correct technical and editorial
errors. These amendments address issues raised by the Coke Oven
Environmental Task Force, including an alternate sulfur dioxide
(SO2) limit during SO2 control system maintenance
and allowing the use of parametric monitoring of nitrogen oxide
(NOX) emissions for owners and operators of coke oven gas-
fired (COG) steam generating units. In addition, we are specifying the
opacity monitoring requirements for owners and operators of all
affected facilities that are subject to an opacity limit, including
owner and operators of COG-fired steam generating units, but exempt
from the continuous opacity monitoring system (COMS) requirement. This
action promulgates the amended regulatory language as proposed, except
for those significant provisions identified below.
We are also finalizing several clarifications to correct technical
and editorial errors and to amend the monitoring requirements for
owners and operators of affected facilities that elect to install
particulate matter continuous emission monitoring systems (PM CEMS).
Owners and operators of affected facilities that install a PM CEMS will
be exempt from the opacity standard as long as they are complying with
a federally enforceable permit limiting PM emissions to 0.030 pounds
per million British thermal units or less. In addition, owner and
operators of affected facilities that elect to install PM CEMS will be
required to measure and report emissions of condensable PM.
Minor revisions to the proposed regulatory language were also made
to clarify specific provisions or to correct unintentional technical
omissions and terminology, typographical, printing, and grammatical
errors that were identified in the proposed rule either as a result of
comments we received or based on our own subsequent review of the text.
One change revises appropriate definitions and requirements in subpart
Da to clarify the applicability and implementation of the subpart Da
provisions to integrated coal gasification combined cycle electric
utility power plants. Another change clarifies the fact that not all
combined cycle facilities that burn solid derived fuels are subject to
the subpart.
The final amendments promulgated by this action reflect EPA's
consideration of the comments received on the proposal. EPA's responses
to the substantive public comments on the proposal are presented in a
comment summary and response document available in Docket ID No. EPA-
HQ-OAR-2005-0031. A summary of selected public comments and our
responses is as follows.
Comment: Several commenters generally support the exemption of
affected facilities using PM CEMS from the opacity standard. However,
the commenters requested that EPA exempt those affected facilities
opting to use PM CEMS from the opacity standard without imposing
conditions for additional condensable PM or opacity tests. The
commenters stated the EPA's proposed method for measuring condensable
PM (Method 202) is flawed and significantly overstates the amount of
condensable PM, and noted that Method 202 itself condenses gaseous
emissions that would not be condensing in the flue gas. They also noted
that further improvements of Method 202 must be made before it is
required as the method to measure condensable PM.
Response: The opacity standard and all opacity monitoring
requirements have been eliminated for owner/operators of affected
facilities complying with a federally enforceable PM limit of 0.030 lb/
MMBtu or less who voluntarily elect to use a PM CEMS to demonstrate
continuous compliance with the PM limit. The contribution of filterable
PM to opacity at these emission levels is generally negligible, and
sources with mass limits at this level or less will operate with little
or no visible emissions (i.e. less than 5 percent opacity). As a
result, EPA believes that an opacity standard is no longer necessary
for these sources since the PM mass emission rate standard is
substantially tighter than the opacity standard and the mass of PM
emissions will be continually monitored.
We concluded, however, that it is only appropriate to eliminate the
opacity standard and associated opacity monitoring for owners/operators
of facilities complying with a PM limit of
[[Page 5074]]
0.030 lb/MMBtu or less. At this emission rate, the presence of visible
emissions may indicate that the PM control device is not operating
properly. This amended NSPS does not require any corrective action in
such a case as long as the PM CEMS is complying with all applicable
federal requirements. However, PM CEMS readings cannot be verified as
readily as other CEMS, and since recalibration requires PM performance
tests, baseline opacity readings can be a valuable secondary check on
control device performance and PM emissions. The local permitting
authority does have the discretion to require an investigation to
determine the cause of the visible emissions. The presence of such
emissions is not, however, necessarily evidence of a violation of the
PM standard. In situations where the owner/operator of a facility has
documented visible emissions during the initial or subsequent PM CEMS
calibration testing or documented trends in PM CEMS readings that
correlate to the visible emissions, the relative amount of visible
emissions can still be used by the local permitting authority as a
secondary check that both the PM control device and PM CEMS are
operating properly. While these facilities will not be required to
install continuous opacity monitoring systems (COMS), if a facility
decided to or is required by the permitting authority to install a
COMS, the data would be useful as a secondary check on PM emissions and
proper operation of the PM control device and to verify that the PM
CEMS is operating properly. Owners/operators of affected facilities
with a PM limit greater than 0.030 lb/MMBtu that elect to install PM
CEMS may have some visible emissions, will still be subject to an
opacity limit, and will be required to either use a COMS or perform
periodic visual inspections to comply with the opacity standard.
In addition, we have concluded it is appropriate to require
condensable PM testing for owners/operators of affected facilities that
elect to use PM CEMS to determine the contribution of condensable PM to
total PM emissions. We will use this data to determine if the
condensable PM emissions from steam generating units have a significant
health and/or environmental impact and whether condensable PM should be
included in future amendments to the PM standard. By early 2009, we
intend to propose amendments to Method 202 that will address the
concerns about artifact measurement. Since the rule will not be
finalized until early in 2010, we are delaying the requirement to
perform condensable PM testing until July 1, 2010 or until Method 202
is revised to minimize artifact measurement, whichever is later.
Comment: Several commenters oppose increasing the Method 9
monitoring frequency. The commenters stated that increasing the
frequency from annually to a weekly, monthly, or quarterly basis
without identifying any particular issue of concern that might occur on
a weekly, monthly, or quarterly basis is arbitrary, unnecessary, overly
burdensome, and would provide little environmental benefit. In
addition, one commenter supports the use of Method 22 as an alternative
to Method 9 for those sources that are expected to have no significant
visible emissions. However, three 1-hour Method 22 observations would
actually take significantly longer than 3 hours. Under Method 22,
observers are instructed not to continuously view emissions for more
than 15-20 minutes at a time, and that breaks of 5-10 minutes should be
taken between each observation. Following these criteria, each 1-hour
observation would take at least one and a half hours. Finally, one
commenter requested that EPA allow for owners/operators of affected
facilities that comply with subpart D, Da, Db, or Dc, by the use of a
fabric filter, the alternative of installing and operating
triboelectric bag leak detectors as an alternative to using a COMS.
Response: We have concluded that the appropriate approach is to
base the frequency of visible emissions monitoring on the level of
visible emissions detected during the most recent observation. Owners/
operators of facilities that elect to not use a COMS to demonstrate
compliance with the opacity limit will conduct at least an initial
Method 9 performance test. The frequency of the required subsequent
Method 9 testing is based on the results of the highest 6-minute
opacity observed during the most recent performance test. Owners/
operators of affected facilities where the maximum 6-minute opacity
reading is greater than 10 percent will be required to conduct monthly
Method 9 performance testing; owners/operators of affected facilities
where the maximum 6-minute opacity reading is between 5 percent and 10
percent will be required to conduct quarterly Method 9 performance
testing; owners/operators of affected facilities with some visible
emissions but where the maximum 6-minute opacity reading is 5 percent
or less will be required to conduct semi-annual Method 9 performance
testing; and owners/operators of affected facilities with no visible
emissions will only be required to conduct an annual Method 9
performance test.
As an alternative, owners/operators of affected facilities where
maximum 6-minute opacity readings from the most recent Method 9
performance test is less than 10 percent may elect to use either Method
22 or the digital opacity monitoring system in lieu of subsequent
Method 9 performance testing. The proposed amendments required a total
of 3 hours of observation annually, but did not specify when or for how
long those observations would be done. We have concluded it is
appropriate to decrease the length of each observation to a minimum of
10 minutes, but to increase the frequency to daily observations. This
approach both minimizes the burden of this option while increasing
protection to the environment, as observations will be performed
throughout the year. If an owner/operator of an affected facility
observes visible emissions in excess of 5 percent during any
observation and is unable to take corrective action, they will be
required to either conduct a Method 9 performance test with the
previously specified frequency or to install a COMS. To maintain
consistency in the operation of the digital opacity monitoring system,
the EPA Administrator will approve opacity monitoring plans for owners/
operators that elect to use the digital opacity monitoring system to
detect the presence of visible emissions.
Finally, we have concluded it is appropriate to allow owners/
operators of affected facilities subject to subparts Da, Db, and Dc,
and who install, maintain, and operate a bag leak detection system, the
option to use periodic visual inspections of plume opacity as an
alternative to monitoring opacity with a COMS. Modern baghouses often
operate with no visible emissions, and a bag leak detection system will
allow owners/operators to identify potential problems with the control
device and repair the problems prior to increases in opacity.
Comment: Several commenters oppose the proposed requirement to
electronically submit performance evaluation test date to EPA's WebFIRE
database. One commenter stated that EPA has not: (1) Provided any
rationale for requiring the data to be reported and entered
electronically; (2) provided any information on the proposed reporting
format or mechanism to allow interested parties to understand what sort
of burden this requirement would impose and whether the requirement is
more or less burdensome than other forms of reporting; or (3) provided
any mechanism for sources to confirm the
[[Page 5075]]
authenticity of data submitted to this Web site for their facility.
Furthermore, before EPA can impose any new reporting requirement, EPA
must comply with the requirements of the Paperwork Reduction Act and
also address whether the submission meets the requirements of the
Cross-Media Electronic Reporting Rule (CROMERR), which is codified at
40 CFR part 3. Another commenter stated that any reporting should not
be required of sources until the WebFIRE is fully operational. A formal
regulation is not the proper venue to ``troubleshoot'' communications
with an external database for the regulated community.
Response: EPA does not expect WebFIRE and the associated Electronic
Reporting Tool (ERT) to be operational until early 2011, and we are
delaying the requirement until July 1, 2011. We do not expect
electronic submittal of performance test information to have any
significant costs or impacts to industry (because we are not requiring
additional testing or software and source testing companies already
compile these data electronically), and since submission of data
directly to EPA is only a requirement for facilities that voluntary
elect to use PM CEMS to demonstrate compliance with the PM limit, the
ICR does not need to be amended. In addition, as an alternate to using
the ERT we are allowing owner/operators to mail the test report
directly to EPA. Finally, we fully expect the ERT to be compliant with
CROMERR before reporting is required in 2011.
Comment: Two commenters requested that EPA reconsider the Agency's
decision to include direct contact water heaters in the definition of
``steam generating unit'' used for determining applicability of the
requirements under subparts Db and Dc because it is contrary to
previous EPA applicability determinations, and it is confusing to
include water heaters in a regulation for steam generating units.
Response: The definition of steam generating unit includes direct
contact water heaters and as such, these units meet the applicability
of subpart Dc. However, we recognize that two source-specific letters
exempt individual direct contact water heaters from the applicability
of subpart Dc of 40 CFR part 60, and owners/operators of the units in
question reasonably relied on these determinations and have not been
complying with subpart Dc to date. We do not intend to reverse these
source specific determinations or to require retroactive reporting for
any owner/operators of similar facilities that relied on these
determinations and have not been maintaining the proper records, but we
are clarifying and confirming that direct contact water heaters have
always been subject to subpart Dc, and records shall be maintained from
June 12, 2008 onward, consistent with the definition of steam
generating unit.
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
Under Executive Order 12866 (58 FR 51735, October 4, 1993), this
action is a ``significant regulatory action'' because it may raise
novel legal or policy issues arising out of legal mandates, the
President's priorities, or the principles set forth in the Executive
Order. Accordingly, EPA submitted this action to the Office of
Management and Budget (OMB) for review under Executive Order 12866 and
any changes made in response to OMB recommendations have been
documented in the docket for this action.
B. Paperwork Reduction Act
This action does not impose any new information collection burden.
The final rule results in no changes to the information collection
requirements of the existing standards of performance and will have no
impact on the information collection estimate of projected cost and
hour burden made and approved by the OMB during the development of the
existing standards of performance. Therefore, the information
collection requests have not been amended. However, OMB previously
approved the information collection requirements contained in the
existing regulations (subparts Da, Db, and Dc of 40 CFR part 60) under
the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq.,
and has assigned OMB control numbers 2060-0023 for subpart Da of 40 CFR
part 60, 2060-0072 for subpart Db of 40 CFR part 60, and 2060-0202 for
subpart Dc of 40 CFR part 60. OMB control numbers for EPA's regulations
in 40 CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act 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 the final amendments on
small entities, small entity is defined as: (1) A small business as
defined by the Small Business Administration's 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.
After considering the economic impacts of this final rule on small
entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities. In
determining whether a rule has a significant economic impact on a
substantial number of small entities, the impact of concern is any
significant adverse economic impact on small entities, since the
primary purpose of the regulatory flexibility analyses is to identify
and address regulatory alternatives ``which minimize any significant
economic impact of the rule on small entities.'' 5 U.S.C. 603 and 604.
Thus, an agency may certify that a rule will not have a significant
economic impact on a substantial number of small entities if the rule
relieves regulatory burden, or otherwise has a positive economic effect
on all of the small entities subject to the rule.
EPA is minimizing the opacity monitoring requirements for owner/
operators of affected facilities subject to an opacity standard but
exempt from the COMS requirement. We have therefore concluded that this
final rule will relieve regulatory burden for all affected small
entities.
D. Unfunded Mandates Reform Act
This rule does not change the overall cost of the rule and
therefore does not contain a Federal mandate that may result in
expenditures of $100 million or more for State, local, and trial
governments, in the aggregate, or the private sector in any 1 year.
Thus, this final rule is not subject to the requirements of sections
202 or 205 of UMRA.
This 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 rule modifies
previously established requirements and does not impose any new
obligations or enforceable duties on any small governments.
[[Page 5076]]
E. Executive Order 13132: Federalism
Executive Order 13132, entitled ``Federalism'' (64 FR 43255, August
10, 1999), requires EPA to develop an accountable process to ensure
``meaningful and timely input by State and local officials in the
development of regulatory policies that have federalism implications.''
``Policies that have federalism implications'' is defined in the
Executive Order to include regulations that have ``substantial direct
effects on the States, on the relationship between the national
government and the States, or on the distribution of power and
responsibilities among the various levels of government.''
This final rule 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 on the distribution
of power and responsibilities among the various levels of government,
as specified in Executive Order 13132. This action will not impose
substantial direct compliance costs on State or local governments; it
will not preempt State law. Thus, Executive Order 13132 does not apply
to this rule.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications, as specified in
Executive Order 13175 (65 FR 67249, November 9, 2000). While utility
steam generating units are located on tribal lands, EPA is not aware of
any that are owned by tribal governments. Thus, Executive Order 13175
does not apply to this action.
G. Executive Order 13045: Protection of Children From Environmental
Health and Safety Risks
EPA interprets Executive Order 13045 (62 FR 19885, April 23, 1997)
as applying to those regulatory actions that concern health or safety
risks, such that the analysis required under section 5-501 of the
Executive Order has the potential to influence the regulation. This
action is not subject to Executive Order 13045 because it is based
solely on technology performance.
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not a ``significant energy action'' as defined in
Executive Order 13211 (66 FR 28355, May 22, 2001) because it is not
likely to have a significant adverse effect on the supply,
distribution, or use of energy. We have concluded that this final rule
is not likely to have any adverse energy effects because it generally
only clarifies our intent and corrects errors in the existing rule.
I. National Technology Transfer Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA''), Public Law 104-113 (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. Voluntary consensus standards
are technical standards (e.g., materials specifications, test methods,
sampling procedures, and business practices) that are developed or
adopted by voluntary consensus standards bodies. NTTAA directs EPA to
provide Congress, through OMB, explanations when the Agency decides not
to use available and applicable voluntary consensus standards.
This final rule involves technical standards. EPA has decided to
use ASTM D975-08a, ``Standard Specification for Diesel Fuel Oils,'' for
defining diesel fuel oil. This standard is available from the American
Society for Testing and Materials (ASTM), 100 Barr Harbor Drive, Post
Office Box C700, West Conshohocken, PA 19428-2959.
EPA has also decided to use EPA Method 202 (40 CFR part 51,
appendix M). The Agency has not found any alternative methods. The
search and review results are in the docket for this regulation.
Under 40 CFR 60.13(i) of the NSPS General Provisions, a source may
apply to EPA for permission to use alternative test methods or
alternative monitoring requirements in place of any required testing
methods, performance specifications, or procedures in the final rule
and amendments.
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 Federal agencies, to the greatest extent practical 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 final rule will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations because it does not
affect the level of protection provided to human health or the
environment. This action does not change any emission limits and,
therefore, does not affect the level of protection provided to human
health or the environment.
H. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801, et seq., as added by
the Small Business Regulatory Enforcement Fairness Act of 1996,
generally provides that before a rule may take effect, the agency
promulgating the rule must submit a rule report, which includes a copy
of the rule, to each House of Congress and to the Comptroller General
of the United States. EPA will submit a report containing these final
amendments and other required information to the U.S. Senate, the U.S.
House of Representatives, and the Comptroller General of the United
States prior to publication of the final rules in the Federal Register.
A major rule cannot take effect until 60 days after it is published in
the Federal Register. This action is not a ``major rule'' as defined by
5 U.S.C. 804(2). This final rule will be effective on January 28, 2009.
List of Subjects in 40 CFR Part 60
Environmental protection, Administrative practice and procedure,
Air pollution control, Incorporation by reference, Intergovernmental
relations, Reporting and recordkeeping requirements.
Dated: November 26, 2008.
Stephen L. Johnson,
Administrator.
Editorial Note: This document was received in the Office of the
Federal Register on Thursday, January 8, 2009.
0
For the reasons stated in the preamble, title 40, chapter I, part 60 of
the Code of Federal Regulations is amended as follows:
PART 60--[AMENDED]
0
1. The authority citation for part 60 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart A--[Amended]
0
2. Section 60.17 is amended by redesignating paragraphs (a)(17) through
(a)(92) as paragraphs (a)(18) through (a)(93) and by adding new
paragraph (a)(17) to read as follows:
[[Page 5077]]
Sec. 60.17 Incorporations by Reference.
* * * * *
(a) * * *
(17) ASTM D975-08a, Standard Specification for Diesel Fuel Oils,
IBR approved for Sec. Sec. 60.41b of subpart Db of this part and
60.41c of subpart Dc of this part.
* * * * *
Subpart D--[Amended]
0
3. Section 60.42 is amended by adding paragraph (c) to read as follows:
Sec. 60.42 Standard for particulate matter (PM).
* * * * *
(c) As an alternate to meeting the requirements of paragraph (a) of
this section, an owner or operator that elects to install, calibrate,
maintain, and operate a continuous emissions monitoring systems (CEMS)
for measuring PM emissions can petition the Administrator (in writing)
to comply with Sec. 60.42Da(a) of subpart Da of this part. If the
Administrator grants the petition, the source will from then on (unless
the unit is modified or reconstructed in the future) have to comply
with the requirements in Sec. 60.43Da(a) of subpart Da of this part.
0
4. Section 60.43 is amended by revising paragraph (d) to read as
follows:
* * * * *
Sec. 60.43 Standard for sulfur dioxide (SO2).
(d) As an alternate to meeting the requirements of paragraphs (a)
and (b) of this section, an owner or operator can petition the
Administrator (in writing) to comply with Sec. 60.43Da(i)(3) of
subpart Da of this part or comply with Sec. 60.42b(k)(4) of subpart Db
of this part, as applicable to the affected source. If the
Administrator grants the petition, the source will from then on (unless
the unit is modified or reconstructed in the future) have to comply
with the requirements in Sec. 60.43Da(i)(3) of subpart Da of this part
or Sec. 60.42b(k)(4) of subpart Db of this part, as applicable to the
affected source.
0
5. Section 60.45 is amended to read as follows:
0
a. By revising paragraph (a);
0
b. By revising paragraphs (b)(1) and (b)(6)(i)(C) and adding paragraph
(b)(7);
0
c. By revising paragraphs (g)(2), (g)(3), and (g)(4); and
0
d. By adding paragraph (h).
Sec. 60.45 Emissions and fuel monitoring.
(a) Each owner or operator shall install, calibrate, maintain, and
operate continuous opacity monitoring system (COMS) for measuring
opacity and a CEMS for measuring SO2 emissions, NOX emissions, and
either oxygen (O2) or carbon dioxide (CO2) except as provided in
paragraph (b) of this section.
(b) * * *
(1) For a fossil-fuel-fired steam generator that burns only gaseous
or liquid fossil fuel (excluding residual oil) with potential SO2
emissions rates of 26 ng/J (0.060 lb/MMBtu) or less and that does not
use post-combustion technology to reduce emissions of SO2 or PM, CEMS
for measuring the opacity of emissions and SO2 emissions are not
required if the owner or operator monitors SO2 emissions by fuel
sampling and analysis or fuel receipts.
* * * * *
(6) * * *
(i) * * *
(C) At a minimum, valid 1-hour CO emissions averages must be
obtained for at least 90 percent of the operating hours on a 30-day
rolling average basis. The 1-hour averages are calculated using the
data points required in Sec. 60.13(h)(2).
* * * * *
(7) The owner or operator of an affected facility subject to an
opacity standard under Sec. 60.42 and that elects to not install a
COMS because the affected facility burns only fuels as specified under
paragraph (b)(1) of this section, monitors PM emissions as specified
under paragraph (b)(5) of this section, or monitors CO emissions as
specified under paragraph (b)(6) of this section shall conduct a
performance test using Method 9 of appendix A-4 of this part and the
procedures in Sec. 60.11 to demonstrate compliance with the applicable
limit in Sec. 60.42 and shall comply with either paragraphs (b)(7)(i),
(b)(7)(ii), or (b)(7)(iii) of this section. If during the initial 60
minutes of observation all 6-minute averages are less than 10 percent
and all individual 15-second observations are less than or equal to 20
percent, the observation period may be reduced from 3 hours to 60
minutes.
(i) Except as provided in paragraph (b)(7)(ii) or (b)(7)(iii) of
this section, the owner or operator shall conduct subsequent Method 9
of appendix A-4 of this part performance tests using the procedures in
paragraph (b)(7) of this section according to the applicable schedule
in paragraphs (b)(7)(i)(A) through (b)(7)(i)(D) of this section, as
determined by the most recent Method 9 of appendix A-4 of this part
performance test results.
(A) If no visible emissions are observed, a subsequent Method 9 of
appendix A-4 of this part performance test must be completed within 12
calendar months from the date that the most recent performance test was
conducted;
(B) If visible emissions are observed but the maximum 6-minute
average opacity is less than or equal to 5 percent, a subsequent Method
9 of appendix A-4 of this part performance test must be completed
within 6 calendar months from the date that the most recent performance
test was conducted;
(C) If the maximum 6-minute average opacity is greater than 5
percent but less than or equal to 10 percent, a subsequent Method 9 of
appendix A-4 of this part performance test must be completed within 3
calendar months from the date that the most recent performance test was
conducted; or
(D) If the maximum 6-minute average opacity is greater than 10
percent, a subsequent Method 9 of appendix A-4 of this part performance
test must be completed within 30 calendar days from the date that the
most recent performance test was conducted.
(ii) If the maximum 6-minute opacity is less than 10 percent during
the most recent Method 9 of appendix A-4 of this part performance test,
the owner or operator may, as an alternative to performing subsequent
Method 9 of appendix A-4 of this part performance test, elect to
perform subsequent monitoring using Method 22 of appendix A-7 of this
part according to the procedures specified in paragraphs (b)(7)(ii)(A)
and (B) of this section.
(A) The owner or operator shall conduct 10 minute observations
(during normal operation) each operating day the affected facility
fires fuel for which an opacity standard is applicable using Method 22
of appendix A-7 of this part and demonstrate that the sum of the
occurrences of any visible emissions is not in excess of 5 percent of
the observation period (i.e., 30 seconds per 10 minute period). If the
sum of the occurrence of any visible emissions is greater than 30
seconds during the initial 10 minute observation, immediately conduct a
30 minute observation. If the sum of the occurrence of visible
emissions is greater than 5 percent of the observation period (i.e., 90
seconds per 30 minute period) the owner or operator shall either
document and adjust the operation of the facility and demonstrate
within 24 hours that the sum of the occurrence of visible emissions is
equal to or less than 5 percent during a 30 minute observation (i.e.,
90 seconds) or conduct a new Method 9 of appendix A-4 of this part
performance test using the procedures
[[Page 5078]]
in paragraph (b)(7) of this section within 30 calendar days according
to the requirements in Sec. 60.46(b)(3).
(B) If no visible emissions are observed for 30 operating days
during which an opacity standard is applicable, observations can be
reduced to once every 7 operating days during which an opacity standard
is applicable. If any visible emissions are observed, daily
observations shall be resumed.
(iii) If the maximum 6-minute opacity is less than 10 percent
during the most recent Method 9 of appendix A-4 of this part
performance test, the owner or operator may, as an alternative to
performing subsequent Method 9 of appendix A-4 performance tests, elect
to perform subsequent monitoring using a digital opacity compliance
system according to a site-specific monitoring plan approved by the
Administrator. The observations shall be similar, but not necessarily
identical, to the requirements in paragraph (b)(7)(ii) of this section.
For reference purposes in preparing the monitoring plan, see OAQPS
``Determination of Visible Emission Opacity from Stationary Sources
Using Computer-Based Photographic Analysis Systems.'' This document is
available from the U.S. Environmental Protection Agency (U.S. EPA);
Office of Air Quality and Planning Standards; Sector Policies and
Programs Division; Measurement Policy Group (D243-02), Research
Triangle Park, NC 27711. This document is also available on the
Technology Transfer Network (TTN) under Emission Measurement Center
Preliminary Methods.
* * * * *
(g) * * *
(2) Sulfur dioxide. Excess emissions for affected facilities are
defined as:
(i) For affected facilities electing not to comply with Sec.
60.43(d), any three-hour period during which the average emissions
(arithmetic average of three contiguous one-hour periods) of
SO2 as measured by a CEMS exceed the applicable standard in
Sec. 60.43; or
(ii) For affected facilities electing to comply with Sec.
60.43(d), any 30 operating day period during which the average
emissions (arithmetic average of all one-hour periods during the 30
operating days) of SO2 as measured by a CEMS exceed the
applicable standard in Sec. 60.43. Facilities complying with the 30-
day SO2 standard shall use the most current associated
SO2 compliance and monitoring requirements in Sec. Sec.
60.48Da and 60.49Da of subpart Da of this part or Sec. Sec. 60.45b and
60.47b of subpart Db of this part, as applicable.
(3) Nitrogen oxides. Excess emissions for affected facilities using
a CEMS for measuring NOX are defined as:
(i) For affected facilities electing not to comply with Sec.
60.44(e), any three-hour period during which the average emissions
(arithmetic average of three contiguous one-hour periods) exceed the
applicable standards in Sec. 60.44; or
(ii) For affected facilities electing to comply with Sec.
60.44(e), any 30 operating day period during which the average
emissions (arithmetic average of all one-hour periods during the 30
operating days) of NOX as measured by a CEMS exceed the
applicable standard in Sec. 60.44. Facilities complying with the 30-
day NOX standard shall use the most current associated
NOX compliance and monitoring requirements in Sec. Sec.
60.48Da and 60.49Da of subpart Da of this part.
(4) Particulate matter. Excess emissions for affected facilities
using a CEMS for measuring PM are defined as any boiler operating day
period during which the average emissions (arithmetic average of all
operating one-hour periods) exceed the applicable standards in Sec.
60.42. Affected facilities using PM CEMS must follow the most current
applicable compliance and monitoring provisions in Sec. Sec. 60.48Da
and 60.49Da of subpart Da of this part.
(h) The owner or operator of an affected facility subject to the
opacity limits in Sec. 60.42 that elects to monitor emissions
according to the requirements in Sec. 60.45(b)(7) shall maintain
records according to the requirements specified in paragraphs (h)(1)
through (3) of this section, as applicable to the visible emissions
monitoring method used.
(1) For each performance test conducted using Method 9 of appendix
A-4 of this part, the owner or operator shall keep the records
including the information specified in paragraphs (h)(1)(i) through
(iii) of this section.
(i) Dates and time intervals of all opacity observation periods;
(ii) Name, affiliation, and copy of current visible emission
reading certification for each visible emission observer participating
in the performance test; and
(iii) Copies of all visible emission observer opacity field data
sheets;
(2) For each performance test conducted using Method 22 of appendix
A-4 of this part, the owner or operator shall keep the records
including the information specified in paragraphs (h)(2)(i) through
(iv) of this section.
(i) Dates and time intervals of all visible emissions observation
periods;
(ii) Name and affiliation for each visible emission observer
participating in the performance test;
(iii) Copies of all visible emission observer opacity field data
sheets; and
(iv) Documentation of any adjustments made and the time the
adjustments were completed to the affected facility operation by the
owner or operator to demonstrate compliance with the applicable
monitoring requirements.
(3) For each digital opacity compliance system, the owner or
operator shall maintain records and submit reports according to the
requirements specified in the site-specific monitoring plan approved by
the Administrator.
0
6. Section 60.46 is amended by revising paragraph (d)(2) to read as
follows:
Sec. 60.46 Test methods and procedures.
* * * * *
(d) * * *
(2) For Method 5 or 5B of appendix A-3 of this part, Method 17 of
appendix A-6 of this part may be used at facilities with or without wet
FGD systems if the stack gas temperature at the sampling location does
not exceed an average temperature of 160 [deg]C (320 [deg]F). The
procedures of sections 8.1 and 11.1 of Method 5B of appendix A-3 of
this part may be used with Method 17 of appendix A-6 of this part only
if it is used after wet FGD systems. Method 17 of appendix A-6 of this
part shall not be used after wet FGD systems if the effluent gas is
saturated or laden with water droplets.
* * * * *
Subpart Da--[Amended]
0
7. Section 60.40Da is amended by revising paragraphs (a) and (b), and
adding paragraph (e) to read as follows:
Sec. 60.40Da Applicability and designation of affected facility.
(a) Except as specified in paragraph (e) of this section, the
affected facility to which this subpart applies is each electric
utility steam generating unit:
(1) That is capable of combusting more than 73 megawatts (MW) (250
million British thermal units per hour (MMBtu/hr)) heat input of fossil
fuel (either alone or in combination with any other fuel); and
(2) For which construction, modification, or reconstruction is
commenced after September 18, 1978.
(b) An IGCC electric utility steam generating unit (both the
stationary combustion turbine and any associated duct burners) is
subject to this part and is not subject to subpart GG or KKKK of this
part if both of the conditions specified in paragraphs (b)(1) and (2)
of this section are met.
[[Page 5079]]
(1) The IGCC electric utility steam generating unit is capable of
combusting more than 73 MW (250 MMBtu/hr) heat input of fossil fuel
(either alone or in combination with any other fuel); and
(2) The IGCC electric utility steam generating unit commenced
construction, modification, or reconstruction after February 28, 2005.
* * * * *
(e) Applicability of the requirement of this subpart to an electric
utility combined cycle gas turbine other than an IGCC electric utility
steam generating unit is as specified in paragraphs (e)(1) and (2) of
this section.
(1) Heat recovery steam generators used with duct burners and
associated with an electric utility combined cycle gas turbine that are
capable of combusting more than 73 MW (250 MMBtu/hr) heat input of
fossil fuel are subject to this subpart except in cases when the heat
recovery steam generator meets the applicability requirements and is
subject to subpart KKKK of this part.
(2) For heat recovery steam generators use with duct burners
subject to this subpart, only emissions resulting from the combustion
of fuels in the steam generating unit (i.e. duct burners) are subject
to the standards under this subpart. (The emissions resulting from the
combustion of fuels in the stationary combustion turbine engine are
subject to subpart GG or KKK, as applicable, of this part).
0
8. Section 60.41Da is amended by revising the definitions of ``Gross
output,'' ``Integrated gasification combined cycle electric utility
steam generating unit or IGCC electric utility steam generating unit,''
``Natural gas,'' and ``Petroleum'' to read as follows:
Sec. 60.41Da Definitions.
* * * * *
Gross output means the gross useful work performed by the steam
generated and, for an IGCC electric utility steam generating unit, the
work performed by the stationary combustion turbines. For a unit
generating only electricity, the gross useful work performed is the
gross electrical output from the unit's turbine/generator sets. For a
cogeneration unit, the gross useful work performed is the gross
electrical or mechanical output plus 75 percent of the useful thermal
output measured relative to ISO conditions that is not used to generate
additional electrical or mechanical output or to enhance the
performance of the unit (i.e., steam delivered to an industrial
process).
* * * * *
Integrated gasification combined cycle electric utility steam
generating unit or IGCC electric utility steam generating unit means an
electric utility combined cycle gas turbine that is designed to burn
fuels containing 50 percent (by heat input) or more solid-derived fuel
not meeting the definition of natural gas. No solid fuel is directly
burned in the unit during operation.
Natural gas means:
(1) A naturally occurring mixture of hydrocarbon and nonhydrocarbon
gases found in geologic formations beneath the earth's surface, of
which the principal constituent is methane; or
(2) Liquid petroleum gas, as defined by the American Society of
Testing and Materials in ASTM D1835 (incorporated by reference, see
Sec. 60.17); or
(3) A mixture of hydrocarbons that maintains a gaseous state at ISO
conditions. Additionally, natural gas must either be composed of at
least 70 percent methane by volume or have a gross calorific value
between 34 and 43 megajoules (MJ) per dry standard cubic meter (910 and
1,150 Btu per dry standard cubic foot).
* * * * *
Petroleum means crude oil or a fuel derived from crude oil,
including, but not limited to, distillate oil, and residual oil.
* * * * *
0
9. Section 60.42Da is amended by revising paragraph (b) to read as
follows:
Sec. 60.42Da Standard for particulate matter (PM).
* * * * *
(b) On and after the date the initial PM performance test is
completed or required to be completed under Sec. 60.8, whichever date
comes first, no owner or operator subject to the provisions of this
subpart shall cause to be discharged into the atmosphere from any
affected facility any gases which exhibit greater than 20 percent
opacity (6-minute average), except for one 6-minute period per hour of
not more than 27 percent opacity. Owners and operators of an affected
facility that elect to install, calibrate, maintain, and operate a
continuous emissions monitoring system (CEMS) for measuring PM
emissions according to the requirements of this subpart are exempt from
the opacity standard specified in this paragraph b.
* * * * *
0
10. Section 60.48Da is amended to read as follows:
0
a. By revising paragraph (g)(3);
0
b. By revising the first sentence of paragraph (j)(2);
0
c. By revising paragraph (n);
0
d. By revising paragraph (o) introductory text;
0
e. By revising paragraph (o)(1);
0
f. By revising paragraph (o)(2)(ii);
0
g. By revising the last sentence of paragraph (o)(2)(iii);
0
h. By revising paragraphs (o)(2)(iv) and (o)(2)(vi);
0
i. By revising paragraphs (o)(3)(i) and (o)(3)(ii);
0
j. By revising the first sentence of paragraph (o)(3)(iii);
0
k. By revising the last sentence of paragraph (o)(3)(v);
0
l. By revising paragraph (o)(4)(i)(E);
0
m. By revising the first sentence of paragraph (o)(4)(ii);
0
n. By revising paragraphs (o)(4)(ii)(F), (o)(4)(v) and (o)(4)(5);
0
o. By revising paragraph (p) introductory text and (p)(2); and
0
p. By adding paragraph (q).
Sec. 60.48Da Compliance provisions.
* * * * *
(g) * * *
(3) Compliance with applicable daily average PM emission
limitations is determined by calculating the arithmetic average of all
hourly emission rates for PM each boiler operating day, except for data
obtained during startup, shutdown, and malfunction. Averages are only
calculated for boiler operating days that have valid data for at least
18 hours of unit operation during which the standard applies. Instead,
all of the valid hourly emission rates of the operating day(s) not
meeting the minimum 18 hours valid data daily average requirement are
averaged with all of the valid hourly emission rates of the next boiler
operating day with 18 hours or more of valid PM CEMS data to determine
compliance.
* * * * *
(j) * * *
(2) The owner or operator of an affected duct burner may elect to
determine compliance by using the CEMS specified under Sec. 60.49Da
for measuring NOX and oxygen (O2) (or carbon
dioxide (CO2)) and meet the requirements of Sec. 60.49Da. *
* *
* * * * *
(n) Compliance provisions for sources subject to Sec.
60.42Da(c)(1). The owner or operator of an affected facility subject to
Sec. 60.42Da(c)(1) shall calculate PM emissions by multiplying the
average hourly PM output concentration (measured according to the
provisions of Sec. 60.49Da(t)), by the average hourly flow rate
(measured according to the provisions of Sec. 60.49Da(l) or Sec.
60.49Da(m)), and divided by the average hourly gross energy output
(measured according to the provisions of Sec. 60.49Da(k)). Compliance
with the
[[Page 5080]]
emission limit is determined by calculating the arithmetic average of
the hourly emission rates computed for each boiler operating day.
(o) Compliance provisions for sources subject to Sec.
60.42Da(c)(2) or (d). Except as provided for in paragraph (p) of this
section, the owner or operator of an affected facility for which
construction, reconstruction, or modification commenced after February
28, 2005, shall demonstrate compliance with each applicable emission
limit according to the requirements in paragraphs (o)(1) through (o)(5)
of this section.
(1) You must conduct a performance test to demonstrate initial
compliance with the applicable PM emissions limit in Sec.
60.42Da(c)(2) or (d) by the applicable date specified in Sec. 60.8(a).
Thereafter, you must conduct each subsequent performance test within 12
calendar months following the date the previous performance test was
required to be conducted. You must conduct each performance test
according to the requirements in Sec. 60.8 using the test methods and
procedures in Sec. 60.50Da. The owner or operator of an affected
facility that has not operated for 60 consecutive calendar days prior
to the date that the subsequent performance test would have been
required had the unit been operating is not required to perform the
subsequent performance test until 30 calendar days after the next
boiler operating day. Requests for additional 30 day extensions shall
be granted by the relevant air division or office director of the
appropriate Regional Office of the U.S. EPA.
(2) * * *
(ii) You must comply with the quality assurance requirements in
paragraphs (o)(2)(ii)(A) through (E) of this section.
* * * * *
(iii) * * * If your opacity baseline level is less than 5.0
percent, then the opacity baseline level is set at 5.0 percent.
(iv) You must evaluate the preceding 24-hour average opacity level
measured by the COMS each boiler operating day excluding periods of
affected facility startup, shutdown, or malfunction. If the measured
24-hour average opacity emission level is greater than the baseline
opacity level determined in paragraph (o)(2)(iii) of this section, you
must initiate investigation of the relevant equipment and control
systems within 24 hours of the first discovery of the high opacity
incident and take the appropriate corrective action as soon as
practicable to adjust control settings or repair equipment to reduce
the measured 24-hour average opacity to a level below the baseline
opacity level. In cases when a wet scrubber is used in combination with
another PM control device that serves as the primary PM control device,
the wet scrubber must be maintained and operated.
* * * * *
(vi) If the measured 24-hour average opacity for your affected
facility remains at a level greater than the opacity baseline level
after 7 boiler operating days, then you must conduct a new PM
performance test according to paragraph (o)(1) of this section and
establish a new opacity baseline value according to paragraph (o)(2) of
this section. This new performance test must be conducted within 60
days of the date that the measured 24-hour average opacity was first
determined to exceed the baseline opacity level unless a waiver is
granted by the permitting authority.
(3) * * *
(i) You must calibrate the ESP predictive model with each PM
control device used to comply with the applicable PM emissions limit in
Sec. 60.42Da(c)(2) or (d) operating under normal conditions. In cases
when a wet scrubber is used in combination with an ESP to comply with
the PM emissions limit, the wet scrubber must be maintained and
operated.
(ii) You must develop a site-specific monitoring plan that includes
a description of the ESP predictive model used, the model input
parameters, and the procedures and criteria for establishing monitoring
parameter baseline levels indicative of compliance with the PM
emissions limit. You must submit the site-specific monitoring plan for
approval by the permitting authority. For reference purposes in
preparing the monitoring plan, see the OAQPS ``Compliance Assurance
Monitoring (CAM) Protocol for an Electrostatic Precipitator (ESP)
Controlling Particulate Matter (PM) Emissions from a Coal-Fired
Boiler.'' This document is available from the U.S. Environmental
Protection Agency (U.S. EPA); Office of Air Quality Planning and
Standards; Sector Policies and Programs Division; Measurement Policy
Group (D243-02), Research Triangle Park, NC 27711. This document is
also available on the Technology Transfer Network (TTN) under Emission
Measurement Center Continuous Emission Monitoring.
(iii) You must run the ESP predictive model using the applicable
input data each boiler operating day and evaluate the model output for
the preceding boiler operating day excluding periods of affected
facility startup, shutdown, or malfunction. * * *
* * * * *
(v) * * * This new performance test must be conducted within 60
calendar days of the date that the model parameter was first determined
to exceed its baseline level unless a waiver is granted by the
permitting authority.
(4) * * *
(i) * * *
(E) Following initial adjustment, you must not adjust the averaging
period, alarm set point, or alarm delay time without approval from the
permitting authority except as provided in paragraph (d)(1)(vi) of this
section.
* * * * *
(ii) You must develop and submit to the permitting authority for
approval