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, 33642-33659 [E8-12621]
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33642
Federal Register / Vol. 73, No. 114 / Thursday, June 12, 2008 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 60
[EPA–HQ–OAR–2005–0031; FRL–8576–2]
RIN 2060–AO61
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
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: EPA is proposing to amend
the new source performance standards
for electric utility steam generating units
and industrial-commercial-institutional
steam generating units. On June 13,
2007, EPA promulgated amendments to
the standards for steam generating units.
Subsequently, EPA received a petition
for reconsideration which it is granting
to the extent specified in the proposed
action. EPA is proposing to amend
specific provisions in the standards for
steam generating units, as amended, to
resolve issues and questions raised by
the petitioner for reconsideration, and to
correct technical and editorial errors
that have been identified since
promulgation. In addition, EPA is
requesting comment on the appropriate
opacity standard for owners/operators of
affected facilities using a particulate
matter continuous emissions monitoring
system to demonstrate compliance with
the applicable PM limit.
DATES: Comments. Comments must be
received on or before July 28, 2008. If
anyone contacts EPA by June 23, 2008
requesting to speak at a public hearing,
EPA will hold a public hearing on June
27, 2008.
ADDRESSES: Comments. Submit your
comments, identified by Docket ID No.
NAICS 1
Category
mstockstill on PROD1PC66 with PROPOSALS2
EPA–HQ–OAR–2005–0031, by one of
the following methods:
• https://www.regulations.gov. Follow
the on-line instructions for submitting
comments.
• E-mail: a-and-r-docket@epa.gov.
• By Facsimile: (202) 566–1741.
• Mail: Air and Radiation Docket,
U.S. EPA, Mail Code 6102T, 1200
Pennsylvania Ave., NW., Washington,
DC 20460. Please include a total of two
copies. In addition, please mail a copy
of your comments on the information
collection provisions to the Office of
Information and Regulatory Affairs,
Office of Management and Budget
(OMB), Attn: Desk Officer for EPA, 725
17th Street, NW., Washington, DC
20503. EPA requests a separate copy
also be sent to the contact person
identified below (see FOR FURTHER
INFORMATION CONTACT).
• Hand Delivery: EPA Docket Center,
Docket ID Number EPA–HQ–OAR–
2005–0031, EPA West Building, 1301
Constitution Ave., NW., Room 3334,
Washington, DC 20004. Such deliveries
are accepted only during the Docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2005–
0031. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through regulations.gov or email. The https://www.regulations.gov
Web site is an ‘‘anonymous access’’
system, which means EPA will not
know your identity or contact
information unless you provide it in the
body of your comment. If you send an
e-mail comment directly to EPA without
going through https://
www.regulations.gov, your e-mail
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
Industry ....................................................
Federal Government ................................
221112
22112
State/local/tribal government ...................
22112
921150
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made available on the Internet. If you
submit an electronic comment through
https://www.regulations.gov, EPA
recommends that you include your
name and other contact information in
the body of your comment as well as
with any disk or CD–ROM you submit.
If EPA cannot read your comment due
to technical difficulties and cannot
contact you for clarification, EPA may
not be able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses. For additional information
about EPA’s public docket visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Air and Radiation Docket EPA/DC,
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
and Radiation Docket is (202) 566–1742.
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.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
Regulated Entities. Entities potentially
affected by this proposed action
include, but are not limited to, the
following:
Examples of 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 utility steam generating units located in Indian Country.
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Federal Register / Vol. 73, No. 114 / Thursday, June 12, 2008 / Proposed Rules
NAICS 1
Category
Any industrial, commercial, or institutional facility using a steam generating
unit as defined in 60.40b or 60.40c.
1 North
211
321
322
325
324
316, 326, 339
331
332
336
221
622
611
Examples of regulated entities
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
for readers regarding entities likely to be
regulated by the proposed rule. To
determine whether your facility is
regulated by the proposed rule, you
should examine the applicability
criteria in § 60.40a, § 60.40b, or § 60.40c
of 40 CFR part 60. If you have any
questions regarding the applicability of
the proposed rule to a particular entity,
contact the person listed in the
preceding FOR FURTHER INFORMATION
CONTACT section.
WorldWide Web (WWW). Following
the Administrator’s signature, a copy of
the proposed amendments will be
posted on the Technology Transfer
Network’s (TTN) policy and guidance
page for newly proposed or promulgated
rules at https://www.epa.gov/ttn/oarpg.
The TTN provides information and
technology exchange in various areas of
air pollution control.
Public Hearing. If a public hearing is
requested, it will be held at 10 a.m. at
the EPA Facility Complex in Research
Triangle Park, North Carolina or at an
alternate site nearby. Contact Mr.
Christian Fellner at 919–541–4003 to
request a hearing, to request to speak at
a hearing, to determine if a hearing will
be held, or to determine the hearing
location.
Outline. The information presented in
this preamble is organized as follows:
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33643
I. Background
II. Proposed Amendments
A. Opacity Monitoring
B. Additional Proposed Amendments to
Subpart D
C. Additional Proposed Amendments to
Subpart Da
D. Additional Proposed Amendments to
Subpart Db and Dc
III. Rationale for Proposed Amendments
A. Alternate Opacity Monitoring
B. Additional Proposed Amendments to
Subpart Da
C. Additional Proposed Amendments to
Subparts Db and Dc
IV. Opacity Monitoring for Facilities With
PM CEMS
V. Statutory and Executive Order Reviews
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A. Executive Order 12866: Regulatory
Planning and Review
B. Paper 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
I. Background
New source performance standards
(NSPS) implement Clean Air Act (CAA)
section 111(b) and are issued for
categories of sources which have been
identified as causing, or contributing
significantly to, air pollution which may
reasonably be anticipated to endanger
public health or welfare. The primary
purpose of the NSPS are to help States
attain and maintain ambient air quality
by ensuring that the best demonstrated
emission control technologies are
installed as industrial infrastructure is
modernized. Since 1970, the NSPS have
been successful in achieving long-term
emissions reductions in numerous
industries by assuring cost-effective
controls are installed on new,
reconstructed, and modified sources.
CAA section 111 requires that NSPS
reflect the degree of emission limitation
achievable through application of the
best system of emissions reductions
which (taking into consideration the
cost of achieving such emissions
reductions, any non-air quality health
and environmental impact, and energy
requirements) the Administrator
determines has been adequately
demonstrated. This level of control is
commonly referred to as best
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demonstrated technology (BDT). CAA
section 111(b)(1)(B) requires the EPA to
periodically review and revise the
standards of performance, as necessary,
to reflect improvements in methods for
reducing emissions.
We promulgated amendments to the
new source performance standards for
steam generating units (40 CFR part 60,
subparts D, Da, Db, and Dc) on June 13,
2007 (72 FR 32710). The amendments
added compliance alternatives for
owners and operators of certain affected
sources, revised certain recordkeeping
and reporting requirements, corrected
technical and editorial errors, and
updated the grammatical style of the
four subparts to be more consistent
across all four steam generating unit
NSPS.
A petition for reconsideration of the
amendments was filed by the Coke
Oven Environmental Task Force
(COETF), and we have decided to grant
reconsideration of the amendments to
the extent specified in the proposed
rule. The amendments proposed by this
action address specific issues for which
the petitioners requested
reconsideration.
As part of this action, we are also
proposing to specify opacity monitoring
requirements for owners/operators of
affected facilities that are subject to an
opacity limit, but are not required to use
a continuous opacity monitor system
(COMS). In addition, we are proposing
to amend other rule language to correct
technical omissions, typographical
errors, cross-reference errors,
grammatical errors, and various other
issues that have been identified since
promulgation of the previous
amendments. The proposed
amendments would not significantly
change our original projections for the
rule’s compliance costs, environmental
benefits, burden on industry, or the
number of affected facilities.
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Federal Register / Vol. 73, No. 114 / Thursday, June 12, 2008 / Proposed Rules
C. Additional Proposed Amendments to
Subpart Da
II. Proposed Amendments
A. Opacity Monitoring
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We are proposing multiple options to
monitor opacity for owners/operators of
affected facilities that are subject to an
opacity limit, but exempt from the
COMS requirement. Under the first
option, the owner/operator conducts an
annual EPA Method 9 opacity
performance test on each affected
facility to demonstrate compliance with
the applicable opacity limit. A second
option is for the owner/operator to use
annual EPA Method 22 observations in
lieu of Method 9 observations to
demonstrate that the sum of occurrences
of any visible emissions is not in excess
of 5 percent of the observation period.
As a third option, we are proposing the
use of a digital photographic technique
for detecting visible emissions, as an
explicit alternative to Method 22
observations. This proposed rule
references an EPA preliminary method
entitled ‘‘Determination of Visible
Emission Opacity from Stationary
Sources Using Computer-Based
Photographic Analysis Systems’’ found
at https://www.epa.gov/tnn/emc/prelim/
pre-008.pdf. For this third option, the
facility owner/operator would prepare a
site-specific monitoring plan based on
this technology for approval.
Observations using either Method 22 or
the digital photographic technique
demonstrating that the presence of
visible emissions is less than 5 percent
of the observation period would be
sufficient to demonstrate compliance
with the opacity limit. However, if
either the Method 22 observation or the
digital photographic technique shows
the presence of visible emissions in
excess of 5 percent of the observation
period, then the owner/operator would
be required to conduct a Method 9
performance test within 24 hours to
demonstrate compliance with the
opacity limit.
We are also proposing to require
owners/operators of affected facilities
that elect to use PM CEMS to measure
both the filterable and condensable
particulate matter emissions and to take
Method 9 opacity readings during the
initial PM CEMS calibration and
ongoing correlation testing and to
electronically report those results.
B. Additional Proposed Amendments to
Subpart D
We are proposing to exempt owners/
operators of affected facilities subject to
subpart D that burn 500 part per million
(ppm) or less sulfur distillate oil from
the requirement to install a COMS.
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We are proposing several additional
amendments to subpart Da. First, we are
proposing to exempt from the
requirement to install a COMS owners/
operators of affected facilities subject to
subpart Da that burn 500 ppm or less
sulfur distillate oil. Second, we are
proposing to add a provision to
postpone PM performance testing for
owners/operators of affected facilities
that are not operating at the time a PM
performance test is required to be
conducted. The PM performance test
would not be required until after the
affected facility recommences operation.
Finally, we are proposing to add a
provision requiring that owners/
operators of an affected facility
constructed after February 28, 2005 with
a wet scrubber for which the owner/
operator elects to use the opacity
baseline approach to monitor the
performance of their primary PM
control device, to maintain the liquidto-gas flow rate at 90 percent or higher
of the ratio measured during the most
recent PM performance test.
D. Additional Proposed Amendments to
Subpart Db
We are proposing several
amendments to subpart Db. First, since
synthetic natural gas derived from coal
has uncontrolled emissions similar to
those of natural gas, we are proposing
that synthetic natural gas derived from
coal be considered natural gas instead of
coal under the rule. Similarly, since
diesel fuel has emissions similar to
distillate oil, we are proposing to
include diesel fuel in the definition of
distillate oil. Second, we are proposing
to amend the definition of potential
sulfur dioxide emission rate. This will
clarify that owners/operators of boilers
burning gasified coal and oil that has
been desulfurized prior to combustion
are able to claim credit for pretreatment
reductions when using the fuel-based
compliance alternatives. Third, we are
proposing to amend the definition of
steam generating unit to clarify that all
water heaters, regardless of the
mechanism used to heat the water, are
covered by the NSPS. Fourth, we are
proposing to change the definition of
very low sulfur oil from 0.30 weight
percent sulfur to 0.50 weight percent
sulfur for owners/operators of affected
facilities built after February 28, 2005,
that are located in noncontinental areas.
Finally, we are proposing to allow fuel
blending to achieve the optional
numerical sulfur dioxide (SO2) limit.
We are proposing to make several
amendments primarily impacting
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owner/operators of boilers burning coke
oven gas (COG). First, we are proposing
to align the regulatory test with the
intent of the amendments published
June 13, 2007 (72 FR 32710) and extend
the 30-day SO2 limit maintenance
exemption to owners/operators of COGfired boilers constructed prior to
February 28, 2005 to include
maintenance of all SO2 control
technologies in the exemption, and to
require reporting of what maintenance
was performed during the control
device outage. We are also proposing
that owners/operators of affected
facilities burning gasified coal receive
the same nitrogen oxide (NOX)
monitoring options as owners/operators
of affected facilities burning natural gas.
If adopted, this amendment would
provide owners/operators of affected
facilities burning gasified coal the
option to develop a site-specific
monitoring plan as an alternative to
using a NOX CEMS to monitor NOX
emissions.
E. Additional Proposed Amendments to
Subpart Dc
We are proposing several
amendments to subpart Dc. First, since
synthetic natural gas derived from coal
has uncontrolled emissions similar to
those of natural gas, we are proposing
that synthetic natural gas derived from
coal be considered natural gas instead of
coal. Similarly, since diesel fuel has
emissions similar to those of distillate
oil, we are proposing to include diesel
fuel in the definition of distillate oil.
Second, we are proposing to amend the
definition of steam generating unit to
clarify that all water heaters, regardless
of the mechanism used to heat the
water, are covered by the NSPS. Finally,
we are proposing to allow fuel blending
to achieve the optional numerical SO2
limit.
III. Rationale for Proposed
Amendments
A. Alternate Opacity Monitoring
The amendments to the new source
performance standards for steam
generating units promulgated on June
13, 2007 (72 FR 32710) eliminated the
requirement to install and properly
operate a COMS, but not the opacity
standard, for owners/operators of
certain affected facilities. Those affected
facilities include any steam generating
unit using a PM CEMS to demonstrate
compliance with the applicable PM
limit, oil-fired steam generating units
with a carbon monoxide CEMS, steam
generating units firing 500 ppm sulfur
distillate oil or less (subparts Db and Dc
only), and owners/operators monitoring
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Federal Register / Vol. 73, No. 114 / Thursday, June 12, 2008 / Proposed Rules
opacity emissions under a site-specific
plan approved by the permitting
authority (subparts Db and Dc only). We
intended in promulgating the previous
amendments to provide the COMS
exemption to owners/operators of steam
generating units firing 500 ppm sulfur
distillate oil or less across all of the
subparts. However, we only added the
regulatory language to subparts Db and
Dc. The proposed amendments will
implement the intent of the previous
rulemaking by adding the language to
subparts D and Da.
The previous amendments did not
specify the type and frequency of
alternate opacity monitoring for affected
facilities that do not demonstrate
compliance with the opacity limit using
a COMS. Without adding specific
requirements, it would be up to the
permitting authority to determine the
proper level of monitoring. Since the
COMS exemption is only available to
owner/operators of facilities
continuously monitoring parameters
indicative of opacity (i.e., oil-fired
facilities with CO CEMS) or burning
fuels with inherently low opacity (i.e.,
500 ppm sulfur distillate oil-fired
facilities), we are proposing to require
opacity observations be done only every
12 months. However, this does not
prevent the permitting authority, or any
qualified individual, from performing
Method 9 observation at any time to
determine excess opacity. While
Method 9 remains the most reliable
means of determining compliance with
an applicable opacity limit, we are
including Method 22 as an alternative to
Method 9 since it requires an observer,
but not necessarily a certified Method 9
observer. This option is likely to lower
the compliance burden, since an
uncertified observer is able to monitor
the affected facility for any visible
emissions (i.e., not zero). For sources
with multiple stacks, the use of a digital
camera system would also reduce
compliance costs, while still providing
equivalent protection for the
environment.
Due to the potential emissions from
steam generating units, especially utility
size facilities, we are specifically
requesting comment on whether the
frequency of the opacity observations
should be increased and are considering
two alternatives for the final rule. The
first would increase the frequency of
performance testing and require that
Method 9 performance tests be
completed once each calendar month or
once each calendar quarter. The second
alternate approach we are considering
would require the owner/operator to
perform either daily or weekly Method
22 (or digital photographic technique)
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brief observations (i.e., 5 to 15 minutes).
If any visible emissions are detected, the
owner/operator would be required to
conduct a longer (i.e., at least 1 hour)
observation to determine if the sum of
the time visible emissions are present is
less than 5 percent of the observation
period. If the visible emissions are in
excess of 5 percent of the observation
period, then a Method 9 performance
test would be required within 24 hours.
The benefit of the frequent, but brief,
Method 22 approach is that it provides
more assurance than the once a year
approach that the facility is operating
properly, but it still keeps the
compliance burden relatively low.
B. Additional Proposed Amendments to
Subpart Da
We are proposing to delay the
required PM performance test for
facilities that are not operating at the
time such a test is otherwise required
because we have concluded that it is not
beneficial to the environment or
appropriate to require a facility to
operate just to conduct a performance
test. Also, in the June 13, 2007
rulemaking (72 FR 32710), we intended
to include the requirement that owners/
operators of an affected facility
constructed after February 28, 2005 that
employs a wet scrubber who choose to
use a baseline opacity level to monitor
PM control device performance
maintain the liquid to gas ratio of the
scrubber that was used during the most
recent performance test. Since scrubbers
can potentially impact PM emissions,
we have concluded that it is necessary
that the liquid to gas ratio be maintained
at the same or higher level as during the
performance test as part of the
requirement to demonstrate continuous
compliance with the PM limit. This
provision is presently included in the
requirements for owners/operators using
a predictive electrostatic precipitator
(ESP) model to monitor PM control
device performance, and the proposed
amendments update the regulatory text
to reflect the intent of the original
rulemaking.
C. Additional Proposed Amendments to
Subparts Db and Dc
The intent of the alternate numerical
SO2 limit of 0.20 lb SO2/MMBtu added
in the amendments published on
February 27, 2006 (71 FR 9866) was to
provide flexibility to owners/operators
of steam generating units burning fuels
with inherently low sulfur contents. We
are proposing to clarify that fuel
blending with low sulfur fuels (i.e.
natural gas) can be done to achieve the
optional numerical SO2 limit. The use of
fuel blending decreases compliance
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33645
costs for facilities. If a facility gets a
single delivery of fuel with higher than
expected sulfur content, the facility
owner/operator can blend in low sulfur
fuels to achieve the standard.
The proposal also clarifies that the
term steam generating unit includes
units which heat water regardless of
whether the water is heated directly,
indirectly, or as a heat transfer medium.
The preambles to the final subpart Db
rulemakings (November 25, 1986, 51 FR
42768 and 42772) and December 16,
1987 (52 FR 47826) were clear about our
intent to include facilities which
produce hot water without subsequently
converting the water to steam in the
definition of steam generating unit.
Because there continues to be questions
as to whether the definition of steam
generating unit includes direct contact
water heaters, we are taking this
opportunity to confirm that ‘‘steam
generating unit’’ includes any unit that
combusts fuel and heats water, and does
not categorically exclude direct contact
water heaters. This clarification is not
meant to reverse source-specific
applicability determinations that were
issued prior to today. We are also
reaffirming that fuel combustion units
which function as process heaters are
not covered as steam generating units if
their primary purpose is to heat a fluid
in order to initiate or promote a
chemical reaction in which the fluid
itself is a reactant or catalyst. The
heating of water to act as a heat transfer
medium for vaporizing liquid natural
gas, for example, would not generally
meet the definition of a process heater.
The proposed amendments
addressing steam generating units
located in noncontinental areas that
burn distillate oil or residual oil is based
on the fact that oil containing 0.30
weight percent or less sulfur is not
always readily available to owners/
operators of such units, but that 0.50
weight percent sulfur distillate oil and
residual oil are generally available. It
was not the intent of the amendments
published on February 27, 2006 (71 FR
9866) to require owners/operators of oilfired steam generating units located in
noncontinental areas to incur high fuel
transportation costs or to install post
combustion controls on oil-fired boilers.
The proposed amendments to the
definition of very low sulfur oil and the
corresponding low sulfur oil PM
exemption and SO2 limit exemptions
would allow owner/operators of oilfired steam generating units located in
noncontinental areas to demonstrate
compliance with both limits using fuel
receipts.
We are proposing that gasified coal
(including COG) have the same NOX
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monitoring option as natural gas,
distillate oil, and low nitrogen content
residual oil since gasified coal has
uncontrolled NOX emissions similar to
those of natural gas. Even though COG
is a byproduct gas and not generated for
the purposes of creating useful heat, it
is considered coal for the purposes of
subpart Db. In addition, even though the
chemical compositions of COG and
gasified coal that is generated for the
purposes of creating useful heat are
different, both have similar
uncontrolled NOX emission rates.
Because of the specific characteristics
of the steel industry, the current
regulations allow a 30-day exceedance
per year from the SO2 emission limit for
steam generating units constructed after
February 28, 2005 that burn COG
exclusively or in combination with
other gaseous fuels or distillate oil. COG
desulfurization facilities regardless of
when the steam generating units they
serve were constructed require periodic
maintenance, but the coking process
continues during this time, and it is cost
prohibitive to store the COG. Cokemaking facilities would either have to
install a second desulfurization unit or
flare the COG and burn natural gas
during the maintenance period. Of these
two options, the least cost option would
be to flare the COG and use natural gas
during the annual maintenance. This
would result in both increased cost to
the steel industry and increased NOX
emissions without achieving any
reductions in SO2. We are, therefore,
proposing to expand this exemption to
owners/operators of COG-fired boilers
constructed prior to February 28, 2005
and to the use of post-combustion
controls since both pre- and postcombustion controls require
maintenance. We are also proposing to
add a reporting requirement to assure
that any SO2 exceedances are due to
valid maintenance periods.
IV. Opacity Monitoring for Facilities
With PM CEMS
There are several conditions that
result in opacity from steam generating
units. These include emissions of PM,
NOX, and reactions of stack gases in the
atmosphere. However, opacity from
NOX emissions is rare and only occurs
at high NOX emissions rates. All modern
steam generating units have inherent
NOX emissions rates below the level
that would result in opacity emissions.
Therefore, for modern steam generating
units, the primary causes of opacity are
PM and reactions of stack gases that
occur after the gases are discharged to
the atmosphere. PM CEMS detect solid
or liquid PM at the stack conditions,
and COMS detect anything that blocks
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light at the stack conditions. Since PM
CEMS measure filterable PM (PM that is
either in a solid or liquid state at the
stack conditions) and COMS measure
opaque material that can be used as a
surrogate for particulate matter, we
concluded in a previous rulemaking (71
FR 9866) that it is appropriate for
owners/operators of affected facilities
who use a PM CEMS (to demonstrate
compliance with the applicable PM
limit) to eliminate the use of COMS.
However, the opacity standard itself was
not eliminated, and owners/operators of
facilities who elect not to install PM
CEMS are required to continue to use
COMS. Furthermore, it is possible that
an owner/operator of an affected facility
could be in compliance with the opacity
limit in the stack (i.e., COMS
measurements), but that a Method 9
observation could detect plume opacity
violations.
Since opacity data has been used as
a surrogate for PM emissions 1 and since
PM CEMS give a more direct continuous
measurement of the primary pollutant of
interest causing opacity at steam
generating units and provides data in
units of the PM standard, we are
requesting comment on if eliminating
the opacity standard altogether for
owner/operators using PM CEMS would
be appropriate. However, neither a
COMS nor a PM CEMS 2 detects
condensable PM (i.e., PM that is in the
gaseous state at the stack conditions but
that will condense to form solid or
liquid particulate matter at atmospheric
conditions). Therefore, if we were to
adopt this option and eliminate the
opacity requirement for affected
facilities with PM CEMS, we are
proposing to require owners/operators
of an affected facility with a PM CEMS
to measure and electronically report
filterable and condensable PM along
with Method 9 opacity data (Method 9
observations of the plume opacity may
detect the presence of condensable PM)
during the initial and ongoing
calibration of the PM CEMS. With
sufficient data, we will be able to
determine if a relationship exists
between filterable and condensable PM
and opacity and to establish direct or
parametric monitoring approaches for
condensable PM, including those
relying on techniques other than
opacity, and an appropriate condensable
PM limit.
1 Opacity is also used as an indicator of control
device operation and proper maintenance.
2 New PM CEMS are being developed that may
measure condensable PM.
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V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order (EO) 12866 (58 FR
51735, October 4, 1993) and is,
therefore, not subject to review under
the EO. EPA has concluded that the
amendments will not change the costs
or benefits of the rule. However, EPA is
requesting additional comments on the
issue.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. The
proposed amendments result in no
changes to the information collection
requirements of the existing standards
of performance and would 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 has
previously approved the information
collection requirements contained in the
existing regulations (40 CFR part 60,
subparts Da, Db, and Dc) under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq., at the time
the standards were promulgated on June
11, 1979 (40 CFR part 60, subpart Da, 44
FR 33580), November 25, 1986 (40 CFR
part 60, subpart Db, 51 FR 42768), and
September 12, 1990 (40 CFR part 60,
subpart Dc, 55 FR 37674). OMB
assigned OMB control numbers 2060–
0023 for 40 CFR part 60, subpart Da,
2060–0072 for 40 CFR part 60, subpart
Db, and 2060–0202 for 40 CFR part 60,
subpart Dc. The 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 this rule on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administration’s regulations at 13 CFR
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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 proposed rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
This proposed rule will not impose any
requirements on small entities.
We continue to be interested in the
potential impacts of the proposed rule
on small entities and welcome
comments on issues related to such
impacts.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State, local,
and tribal governments, in the aggregate,
or to the private sector, of $100 million
or more in any one year. Before
promulgating an EPA rule for which a
written statement is needed, section 205
of the UMRA generally requires EPA to
identify and consider a reasonable
number of regulatory alternatives and
adopt the least costly, most costeffective or least burdensome alternative
that achieves the objectives of the rule.
The provisions of section 205 do not
apply when they are inconsistent with
applicable law. Moreover, section 205
allows EPA to adopt an alternative other
than the least costly, most cost effective
or least burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
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small governments on compliance with
the regulatory requirements.
EPA has determined that this rule
does not contain a Federal mandate that
may result in expenditures of $100
million or more for State, local, and
tribal governments, in the aggregate, or
the private sector in any one year. Thus,
this rule is not subject to the
requirements of section 202 and 205 of
the UMRA. In addition, EPA determined
that this rule contains no regulatory
requirements that might significantly or
uniquely affect small governments
because the burden is small and the
regulation does not unfairly apply to
small governments. Therefore, this rule
is not subject to the requirements of
section 203 of the UMRA.
E. Executive Order 13132: Federalism
Executive Order (EO) 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 EO 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 proposed 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 EO
13132. These proposed amendments
will not impose substantial direct
compliance costs on State or local
governments; they will not preempt
State law. Thus, EO 13132 does not
apply to this rule. In the spirit of EO
13132, and consistent with EPA policy
to promote communications between
EPA and State and local governments,
EPA specifically solicits comment on
this proposed rule from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
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implications.’’ This proposed rule does
not have tribal implications, as specified
in EO 13175. Thus, EO 13175 does not
apply to this rule. EPA specifically
solicits additional comment on this
proposed rule from tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
EPA interprets EO 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 EO has the potential to influence the
regulation. This proposed rule is not
subject to EO 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 rule is not subject to Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355 (May 22, 2001)) because it is
not a significant regulatory action under
Executive Order 12866.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law No.
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 proposed rulemaking involves
technical standards. EPA proposes to
use ASTM D975–08, ‘‘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.
The 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.
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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. EPA welcomes
comments on this aspect of the
proposed rulemaking and, specifically,
invites the public to identify
potentially-applicable voluntary
consensus standards and to explain why
such standards should be used in this
proposed action.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
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:
§ 60.17
*
*
*
*
(17) ASTM D975–08, Standard
Specification for Diesel Fuel Oils, IBR
approved for §§ 60.41(b) of subpart Db
of this part and 60.41c of subpart Dc of
this part.
*
*
*
*
*
Subpart D—[Amended]
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
proposed rule will not have
disproportionately high adverse human
health or environmental effects on
minority or low-income populations
because it increases the level of
environmental protection for all affected
populations without having any
disproportionately high adverse human
health or environmental effects on any
populations, including any minority or
low-income population.
3. Section 60.43 is amended by
revising paragraph (d) to read as
follows:
§ 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 § 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.
*
*
*
*
*
4. Section 60.45 is amended to read as
follows:
a. By revising paragraph (b)(1) and
adding new paragraph (b)(7); and
b. By revising paragraphs (g)(2),(g)(3),
and (g)(4).
List of Subjects in 40 CFR Part 60
§ 60.45
Environmental protection,
Administrative practice and procedure,
Air pollution control, Incorporation by
reference, Intergovernmental relations,
Reporting and recordkeeping
requirements.
*
Dated: May 30, 2008.
Stephen L. Johnson,
Administrator.
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Incorporations by Reference.
*
For the reasons stated in the
preamble, title 40, chapter I, part 60, of
the Code of the Federal Regulations is
proposed to be 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.
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Emissions and fuel monitoring.
*
*
*
*
(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.
*
*
*
*
*
(7) The owner or operator of an
affected facility subject to an opacity
standard under § 60.42 and that elects to
not install a CEMS for measuring
opacity because the affected facility
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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 comply with either paragraphs
(b)(7)(i), (b)(7)(ii), or (b)(7)(iii) of this
section.
(i) 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. The Method
9 observations must be completed, at a
minimum, every 12 months; or
(ii) Conduct a series of three 1-hour
observations (during normal operation)
using Method 22 of Appendix A–7 of
this part at the affected facility 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., 9 minutes per 3hour period). The Method 22
observations must be completed, at a
minimum, every 12 months. If the sum
of the occurrences of visible emissions
in excess of 5 percent of the observation
period, then the owner or operator shall
conduct a performance test within 24
hours according to the requirements in
§ 60.46(a)(3); or
(iii) Monitor opacity using a digital
opacity compliance system according to
a site-specific monitoring plan approved
by the Administrator. The observations
should include at least one digital image
every 15 seconds for three separate 1hour periods (during normal operation)
every 12 months. An approvable
monitoring plan should include a
demonstration that the occurrences of
visible emissions are not in excess of 5
percent of the observation period (i.e.,
36 observations per 3-hour period). 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. If the sum of the
occurrences of any visible emissions is
in excess of 5 percent of the observation
period, then the owner or operator shall
conduct a new performance test within
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24 hours according to the requirements
in § 60.46(a)(3).
*
*
*
*
*
(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 under § 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
under § 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.
(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 under § 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
under § 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 under § 60.42. Affected
facilities using PM CEMS in lieu of a
CEMS for monitoring opacity emissions
must follow the most current applicable
compliance and monitoring provisions
in §§ 60.48Da and 60.49Da of subpart Da
of this part.
5. Section 60.46 is amended by
revising paragraph (b)(2) introductory
text to read as follows:
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§ 60.46
Test methods and procedures.
*
*
*
*
*
(b) * * *
(2) Method 5 of appendix A–3 of this
part shall be used to determine PM
concentration (C) at affected facilities
without wet flue-gas-desulfurization
(FGD) systems and Method 5B of
appendix A–3 of this part shall be used
to determine the PM concentration (C)
after FGD systems. 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 2.1 and
2.3 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]
6. Section 60.40Da is amended by
revising paragraph (b)(4) to read as
follows:
§ 60.40Da Applicability and designation of
affected facility.
*
*
*
*
*
(b) * * *
(4) Heat recovery steam generators
that are associated with combined cycle
gas turbines that meet the applicability
requirements of subpart KKKK of this
part are not subject to this part. This
subpart will continue to apply to all
other electric utility combined cycle gas
turbines that are capable of combusting
more than 73 MW (250 MMBtu/hr) heat
input of fossil fuel in the heat recovery
steam generator. If the heat recovery
steam generator is subject to this subpart
and the stationary combustion turbine is
subject to either subpart GG or KKKK of
this part, only emissions resulting from
combustion of fuels in the steamgenerating unit are subject to this
subpart. (The stationary combustion
turbine emissions are subject to subpart
GG or KKKK, as applicable, of this part).
*
*
*
*
*
7. Section 60.41Da is amended in
paragraph (c) by revising the definitions
of ‘‘Gross output,’’ ‘‘Petroleum,’’ and
‘‘Potential combustion concentration’’ to
read as follows:
§ 60.41Da
Definitions.
*
*
*
*
*
(c) * * *
Gross output means the gross useful
work performed by the steam generated
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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).
*
*
*
*
*
Petroleum means crude oil or a fuel
derived from crude oil, including, but
not limited to, distillate oil, residual oil,
and petroleum coke.
Potential combustion concentration
means the theoretical emissions
(nanograms per joule (ng/J), lb/MMBtu
heat input) that would result from
combustion of a fuel in an uncleaned
state without emission control systems
and:
*
*
*
*
*
8. Section 60.48Da is amended to read
as follows:
a. By revising paragraph (n);
b. By revising paragraphs (o)
introductory text, (o)(1), (o)(2)(ii)
introductory text, (o)(2)(iii), (o)(2)(iv),
(o)(2)(vi), (o)(3)(i), (o)(3)(iii), and (o)(5);
and
c. By adding paragraph (q).
§ 60.48Da
Compliance provisions.
*
*
*
*
*
(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
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 and § 60.49Da(a)(2), 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
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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.
An affected facility that has not
operated for 2 months prior to the due
date of a performance test is not
required to perform the subsequent
performance test until 60 days after the
next boiler operating day.
(2) * * *
(ii) You must comply with the quality
assurance requirements in paragraphs
(o)(2)(ii)(A) through (E) of this section.
*
*
*
*
*
(iii) During each performance test
conducted according to paragraph (o)(1)
of this section, you must establish an
opacity baseline level. The value of the
opacity baseline level is determined by
averaging all of the 6-minute average
opacity values (reported to the nearest
0.1 percent opacity) from the COMS
measurements recorded during each of
the test run intervals conducted for the
performance test, and then adding 2.5
percent opacity to your calculated
average opacity value for all of the test
runs. 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
alone or in combination with another
PM control device to comply with the
PM emissions limit, the daily average
liquid-to-gas flow rate for the wet
scrubber must be maintained at least at
90 percent of average ratio measured
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during all test run intervals for the
performance test conducted according
to paragraph (o)(1) of this section.
*
*
*
*
*
(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 daily average liquid-to-gas
flow rate for the wet scrubber must be
maintained at least at 90 percent of
average ratio measured during all test
run intervals for the performance test
conducted according to paragraph (o)(1)
of this section.
*
*
*
*
*
(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. If the values for one or
more of the model parameters exceed
the applicable baseline levels
determined according to your approved
site-specific monitoring plan, you must
initiate investigation of the relevant
equipment and control systems within
24 hours of the first discovery of a
model parameter deviation and, take the
appropriate corrective action as soon as
practicable to adjust control settings or
repair equipment to return the model
output to within the applicable baseline
levels.
*
*
*
*
*
(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
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each performance test run as
determined by analysis of the fuel as
fired.
*
*
*
*
*
(q) Compliance provisions for sources
subject to § 60.42Da(b). An owner or
operator of an affected facility subject to
the opacity standard under § 60.42Da(b)
shall meet the requirements in
paragraphs (q)(1) and (2) of this section.
(1) Demonstrate compliance of the
affected facility with the opacity limit in
§ 60.42Da(b) initially and, thereafter,
except as provided in paragraphs
§ 60.49Da(a)(3)(ii) and (iii), at least once
every 12 months according to the
requirements in § 60.50Da(b)(3), and
(2) 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.
9. Section 60.49Da is amended to read
as follows:
a. By revising paragraph (a);
b. By revising paragraph (t);
c. By revising paragraph (u);
d. By revising paragraph (v); and
e. By revising paragraph (w)(2).
§ 60.49Da
Emission monitoring.
(a) An owner or operator of an
affected facility subject to the opacity
standard under § 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 CEMS, and record the output
of the system, for measuring the opacity
of emissions discharged to the
atmosphere (i.e., install, calibrate,
maintain, and operate a COMS). 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 combustion are monitored
(subject to the approval of the
Administrator).
(2) 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
comply with the requirements of
paragraph (a)(3) of this section as an
alternative to the monitoring
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requirements in paragraph (a)(1) of this
section.
(i) The affected facility uses a CEMS
for measuring PM emissions to
demonstrate continuous compliance on
a boiler operating day average with the
emissions limitations under
§§ 60.42Da(a)(1), 60.42Da(c)(1), or
60.42Da(c)(2), and the PM CEMS is
installed, certified, operated, and
maintained on the affected facility
according to the requirements of
paragraph (v) of this section; or
(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 does not use
post-combustion technology (except a
wet scrubber) for reducing PM, SO2, or
carbon monoxide (CO) emissions, burns
only natural gas, gaseous fuels, or fuel
oils that contain less than or equal to
0.30 weight percent sulfur, and is
operated such that emissions of CO to
the atmosphere from the affected facility
are maintained at levels less than or
equal to 1.4 lb/MWh on a boiler
operating day average basis. Owners and
operators of affected facilities electing to
comply with this paragraph must use a
CEMS measuring CO emissions and
demonstrate compliance according to
the procedures specified in paragraph
(u) of this section.
(3) The owner or operator of an
affected facility that meets the
conditions in paragraph (a)(2) of this
section shall monitor the opacity of
emissions discharged from the affected
facility to the atmosphere according to
the requirements in either paragraph
(a)(3)(i), (ii), or (iii) of this section,
(i) 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 limit
in § 60.42Da(b). The Method 9
observations must be completed, at a
minimum, every 12 months; or
(ii) Conduct a series of three 1-hour
observations (during normal operation)
using Method 22 of appendix A–7 of
this part at the affected facility 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., 9 minutes per
3-hour period). The Method 22
observations must be completed, at a
minimum, every 12 months. If the sum
of the occurrences of any visible
emissions is in excess of 5 percent of the
observation period, then the owner or
operator shall conduct a new
performance test within 24 hours
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according to the requirements in
§ 60.50Da(b)(3); or
(iii) Monitor opacity using a digital
opacity compliance system according to
a site-specific monitoring plan approved
by the Administrator. The observations
should include at least one digital image
every 15 seconds for three separate
1-hour periods (during normal
operation) every 12 months. An
approvable monitoring plan should
include a demonstration that the
occurrences of visible emissions are not
in excess of 5 percent of the observation
period (i.e., 36 observations per 3-hour
period). 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. If the sum of the occurrences
of any visible emissions is in excess of
5 percent of the observation period, then
the owner or operator shall conduct a
new performance test within 24 hours
according to the requirements in
§ 60.50Da(b)(3).
*
*
*
*
*
(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 under
§ 60.42Da(a)(1) or § 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
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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.
At least two data points per hour must
be used to calculate each 1-hour
average.
(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)
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.
(1) The owner or operator shall
conduct a performance evaluation of the
CEMS according to the applicable
requirements of § 60.13, Performance
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Specification 11 in appendix B of this
part, and procedure 2 in appendix F of
this part.
(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
conducting performance tests 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) For condensable PM emissions,
Method 202 of appendix M of part 51
shall be used; and
(iii) For visible emissions, Method 9
of Appendix A–4 shall be used; and
(iv) For O2 (or CO2), Method 3, 3A, or
3B of appendix A–2 of this part, as
applicable shall be used.
(3) Quarterly accuracy determinations
and daily calibration drift tests shall be
performed in accordance with
procedure 2 in appendix F of this part.
Relative Response Audits must be
performed annually and Response
Correlation Audits must be performed
every 3 years.
(4) 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 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. If the owner or
operator is unsuccessful in entering the
test data into EPA’s WebFire data base,
then the owner or operator must submit
monthly reports to EPA until the data is
successfully submitted to WebFire. The
monthly reports shall describe the
difficulty preventing successful
submittal of the data and what actions
are being taken to correct the problem.
(w) * * *
(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
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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;
*
*
*
*
*
10. Section 60.50Da is amended by
revising paragraph (f) to read as follows:
§ 60.50Da Compliance determination
procedures and methods.
*
*
*
*
*
(f) Electric utility combined cycle gas
turbines that are not designed and
intended to burn fuels containing 50
percent (by heat input) or more solid
derived fuel not meeting the definition
of natural gas on a 12-month rolling
average 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 from
the gas turbine used in the Method 19
calculations 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.
*
*
*
*
*
Subpart Db—[Amended]
11. Section 60.40b is amended by
revising paragraph (i) to read as follows:
§ 60.40b Applicability and delegation of
authority.
*
*
*
*
*
(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. This
subpart will continue to apply to all
other heat recovery steam generators
that are capable of combusting more
than 29 MW (100 MMBtu/hr) heat input
of fossil fuel. If the heat recovery steam
generator is subject to this subpart, only
emissions resulting from combustion of
fuels in the steam generating unit are
subject to this subpart. (The gas turbine
emissions are subject to subpart GG or
KKKK, as applicable, of this part.)
*
*
*
*
*
12. Section 60.41b is amended in
paragraph by revising the definitions of
‘‘Coal,’’ ‘‘Distillate oil,’’ ‘‘Gaseous fuel,’’
‘‘Gross output,’’ ‘‘Natural gas,’’
‘‘Potential sulfur dioxide emission rate,’’
‘‘Pulverized coal-fired steam generating
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unit,’’ ‘‘Steam generating unit,’’ and
‘‘Very low sulfur oil’’ to read as follows:
§ 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 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
present as 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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rate equal to or less than 215 ng/J (0.50
lb/MMBtu) heat input.
*
*
*
*
*
13. 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), (2),
and (3).
§ 60.42b
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 ∗ H a + Kb ∗ H b )
H a + Hb
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 under 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
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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 under 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.
(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 =
( Kc ∗ H c + Kd ∗ H d )
Hc + Hd
Where:
Es = SO2 emission limit, in ng/J or lb/MMBtu
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 under 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
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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.
*
*
*
*
*
Pulverized coal-fired steam generating
unit means a steam generating unit in
which pulverized coal is introduced
into an air stream that carries the coal
to the combustion chamber of the steam
generating unit where it is fired in
suspension. This includes both
conventional pulverized coal-fired and
micropulverized coal-fired steam
generating units.
*
*
*
*
*
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, an oil
that contains no more than 0.50 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. For
units constructed, reconstructed, or
modified after February 28, 2005 and
not located in a noncontinental area,
very low sulfur oil means an 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 an oil that contains
no more than 0.50 weight percent sulfur
or that, when combusted without SO2
emission control, has a SO2 emission
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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
heat input supplied to the affected
facility from the combustion of coal and
oil is counted under 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), only the heat input
supplied to the affected facility from the
combustion of coal and oil is counted
under 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 60.42b(k)(1).
(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
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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.
*
*
*
*
*
14. Section 60.43b is amended to read
as follows:
a. By revising paragraph (f);
b. By revising paragraphs (h)(1),
(h)(5), and adding new paragraph (h)(6).
§ 60.43b
(PM).
Standard for particulate matter
*
*
*
*
*
(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.
*
*
*
*
*
(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 under § 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
under § 60.43b(h)(1).
(6) On and after the date on which the
initial performance test is completed or
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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 0.50
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 under § 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
under § 60.43b(h)(1).
15. Section 60.44b is amended by
revising paragraph (l)(1) to read as
follows:
§ 60.44
(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
*
*
*
*
*
16. Section 60.45b is amended to read
as follows:
a. By revising paragraph (a);
b. By revising paragraph (d)
introductory text;
c. By revising paragraph (j); and
d. By revising paragraph (k).
§ 60.45b Compliance and performance test
methods and procedures for sulfur dioxide.
(a) The SO2 emission standards under
§ 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.
*
*
*
*
*
(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
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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 under §§ 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 under § 60.49b(r).
17. Section 60.46b is amended to read
as follows:
a. By revising paragraphs (e)(2) and
(e)(4);
b. By revising paragraph (i);
c. By revising paragraphs (j)
introductory text and (j)(11) and adding
new paragraph (j)(14) to read as follows:
§ 60.46b Compliance and performance test
methods and procedures for particulate
matter and nitrogen oxides.
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*
*
*
*
*
(e) * * *
(2) Following the date on which the
initial performance test is completed or
is required to be completed under
§ 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 under § 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 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 under § 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 30-
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day 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.
*
*
*
*
*
(i) The owner or operator of an
affected facility seeking to demonstrate
compliance with the PM limit under
paragraphs § 60.43b(a)(4) or
§ 60.43b(h)(5) shall follow the
applicable procedures under § 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 60minute period) by both the continuous
emission monitors and conducting
performance tests 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) For condensable PM emissions,
Method 202 of appendix M of part 51
shall be used; and
(iii) For visible emissions, Method 9
of Appendix A–4 shall be used; and
(iv) For O2 (or CO2), Method 3, 3A, or
3B of appendix A–2 of this part, as
applicable shall be used.
*
*
*
*
*
(14) 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 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/
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Sfmt 4702
33655
index.cfm?action=fire.main. If the
owner or operator is unsuccessful in
entering the test data into EPA’s
WebFire data base, then the owner or
operator must submit monthly reports to
EPA until the data is successfully
submitted to WebFire. The monthly
reports shall describe the difficulty
preventing successful submittal of the
data and what actions are being taken to
correct the problem.
18. Section 60.47b is amended by
revising paragraphs (a) introductory text
and (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 under § 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.
For units complying with the percent
reduction standard, the SO2 and either
O2 or CO2 concentrations shall both be
monitored at the inlet and outlet of the
SO2 control device. If the owner or
operator has installed and certified SO2
and O2 or CO2 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, those CEMS may be used to
meet the requirements of this section,
provided that:
*
*
*
*
*
(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. 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;
*
*
*
*
*
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19. Section 60.48b is amended to read
as follows:
a. By revising paragraph (a);
b. By revising paragraph (g)
introductory text;
c. By revising paragraph (h)
introductory text; and
d. By revising paragraph (k)
introductory text.
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§ 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 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), or (4) of
this section who elects not to install a
COMS shall comply with either
paragraph (a)(1), (a)(2), or (a)(3) of this
section.
(1) 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. The
Method 9 observations must be
completed, at a minimum, every 12
months; or
(2) Conduct a series of three 1-hour
observations (during normal operation)
using Method 22 of Appendix A–7 of
this part at the affected facility 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., 9 minutes per 3hour period). The Method 22
observations must be completed, at a
minimum, every 12 months. If the sum
of the occurrences of any visible
emissions is in excess of 5 percent of the
observation period, then the owner or
operator shall conduct a new
performance test within 24 hours
according to the requirements in
§ 60.46b(d)(7); or
(3) Monitor opacity using a digital
opacity compliance system according to
a site-specific monitoring plan approved
by the Administrator. The observations
should include at least one digital image
every 15 seconds for three separate 1hour periods (during normal operation)
every 12 months. An approvable
monitoring plan should include a
demonstration that the occurrences of
visible emissions are not in excess of 5
percent of the observation period (i.e.,
36 observations per 3-hour period). For
reference purposes in preparing the
monitoring plan, see OAQPS
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‘‘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. If the sum of the
occurrences of any visible emissions is
in excess of 5 percent of the observation
period, then the owner or operator shall
conduct a new performance test within
24 hours according to the requirements
in § 60.46b(d)(7).
*
*
*
*
*
(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 of
§ 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.
*
*
*
*
*
(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). The CEMS specified in
paragraph § 60.46b(j) 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.
20. Section 60.49b is amended to read
as follows:
a. By revising paragraphs (c)
introductory text and (c)(3);
b. By revising paragraphs (h)
introductory text, (h)(1),(h)(2)
introductory text and (h)(2)(i);
c. By revising paragraph (k)(2); and
d. By revising paragraph (r)
introductory text and(r)(1).
§ 60.49b Reporting and recordkeeping
requirements.
*
*
*
*
*
(c) The owner or operator of each
affected facility subject to the NOX
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standard of § 60.44b who seeks to
demonstrate compliance with those
standards through the monitoring of
steam generating unit operating
conditions under the provisions of
§ 60.48b(g)(2) shall submit to the
Administrator for approval a plan that
identifies the operating conditions to be
monitored under § 60.48b(g)(2) and the
records to be maintained under
§ 60.49b(h). 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 days of the
initial startup of the affected facility or
by May 31, 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(h).
*
*
*
*
*
(h) The owner or operator of any
affected facility in any category listed in
paragraphs (h)(1) or (2) of this section is
required to submit excess emission
reports for any excess emissions that
occurred during the reporting period.
(1) Any affected facility subject to the
opacity standards under § 60.43b(f) or to
the operating parameter monitoring
requirements under § 60.13(i)(1).
(2) Any affected facility that is subject
to the NOX standard of § 60.44b, and
that:
(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;
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Federal Register / Vol. 73, No. 114 / Thursday, June 12, 2008 / Proposed Rules
Subpart Dc—[Amended]
§ 60.42c
21. 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
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*
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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.
*
*
*
*
*
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
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Standard for sulfur dioxide (SO2).
*
Definitions.
*
oil 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.
*
*
*
*
*
22. Section 60.42c is amended by
revising paragraphs (e)(2) and (j) to read
as follows:
*
*
*
*
(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:
Es =
( K a ∗ H a + Kb ∗ H b + Kc ∗ H c )
( H a + Hb + Hc )
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
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
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
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reduction standard, only the heat input
supplied to the affected facility from the
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.
23. 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.
*
*
*
*
*
24. 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 under § 60.48c(f), as
applicable.
*
*
*
*
*
25. Section 60.45c is amended to read
as follows:
a. By revising paragraph (a)(8);
b. By revising paragraphs (c)
introductory text, (c)(7), (c)(8), (c)(9),
(c)(11), and adding new paragraph
(c)(14) to read as follows:
§ 60.45c Compliance and performance test
methods and procedures for particulate
matter.
(a) * * *
(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
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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 under
paragraph 60.45b(a), the report shall
identify the days on which the
maintenance was performed and a
description of the maintenance;
*
*
*
*
*
(r) The owner or operator of an
affected facility who elects to use the
fuel based compliance alternatives in
§ 60.42b or § 60.43b shall either:
(1) The owner or operator of an
affected facility who elects to
demonstrate that the affected facility
combusts only very low sulfur oil and/
or natural gas under § 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 and/or natural gas was
combusted in the affected facility during
the reporting period; or
*
*
*
*
*
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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.
(i) At least two data points per hour
shall be used to calculate each 1-hour
arithmetic average.
(ii) [Reserved]
(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 conducting
performance tests 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) For condensable PM emissions,
Method 202 of appendix M of part 51
shall be used; and
(iii) For visible emissions, Method 9
of Appendix A–4 shall be used; and
(iv) For O2 (or CO2), test Method 3,
3A, or 3B of appendix A–2 of this part,
as applicable shall be used.
*
*
*
*
*
(14) 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 submit the test
data to EPA by successfully entering the
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20:00 Jun 11, 2008
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data electronically into EPA’s WebFire
data base available at https://
cfpub.epa.gov/oarweb/
index.cfm?action=fire.main. If the
owner or operator is unsuccessful in
entering the test data into EPA’s
WebFire data base, then the owner or
operator must submit monthly reports to
EPA until the data is successfully
submitted to WebFire. The monthly
reports shall describe the difficulty
preventing successful submittal of the
data and what actions are being taken to
correct the problem.
*
*
*
*
*
26. Section 60.47c is amended to read
as follows:
a. By revising paragraph (a);
b. By revising paragraph (c)
introductory text;
c. By revising paragraph (d)
introductory text;
d. By revising paragraph (e)
introductory text; and
e. By revising paragraph (f)
introductory text.
§ 60.47c Emission monitoring for
particulate matter.
(a) Except as provided in paragraphs
(c), (d), (e), and (f) 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 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 under
§ 60.43c(c) and that is not required to
install a COMS to measure opacity due
to paragraphs (c), (d), or (e) of this
section that elects not to install a COMS
shall comply with either paragraphs
(a)(1), (a)(2), or (a)(3) of this section.
(1) 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. The Method
9 observations must be completed, at a
minimum, every 12 months; or
(2) Conduct a series of three 1-hour
observations (during normal operation)
using Method 22 of Appendix A–7 of
this part at the affected facility 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., 9 minutes per
3-hour period). The Method 22
observations must be completed, at a
minimum, every 12 months. If the sum
of the occurrences of any visible
emissions is in excess of 5 percent of the
observation period, then the owner or
operator shall conduct a new
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performance test within 24 hours
according to the requirements in
§ 60.45c(a)(8); or
(3) Monitor opacity using a digital
opacity compliance system according to
a site-specific monitoring plan approved
by the Administrator. The observations
should include at least one digital image
every 15 seconds for three separate
1-hour periods (during normal
operation) every 12 months. An
approvable monitoring plan should
include a demonstration that the
occurrences of visible emissions are not
in excess of 5 percent of the observation
period (i.e., 36 observations per 3-hour
period). 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. If the sum of the occurrences
of any visible emissions is in excess of
5 percent of the observation period, then
the owner or operator shall conduct a
new performance test within 24 hours
according to the requirements in
§ 60.450c(a)(8).
*
*
*
*
*
(c) 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
dioxide emission rates of 26 ng/J (0.06
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 under § 60.43c(c) are
not required to operate a CEMS for
measuring opacity if they follow the
applicable procedures under § 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) An affected facility that is subject
to an opacity standard under § 60.43c(c)
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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 0.50 weight percent sulfur,
and is operated such that emissions of
CO 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 for
measuring opacity. 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.
*
*
*
*
*
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(f) An affected facility that is subject
to an opacity standard under § 60.43c(c)
and that burns only gaseous fuels or fuel
oils that contain less than or equal to
0.50 weight percent sulfur and operates
according to a written site-specific
monitoring plan approved by the
permitting authority is not required to
operate a COMS for measuring opacity.
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.
27. Section 60.48c is amended by
revising paragraph (e)(11) to read as
follows:
§ 60.48c Reporting and Recordkeeping
requirements.
*
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*
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*
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(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.
*
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[FR Doc. E8–12621 Filed 6–11–08; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 73, Number 114 (Thursday, June 12, 2008)]
[Proposed Rules]
[Pages 33642-33659]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-12621]
[[Page 33641]]
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Part VI
Environmental Protection Agency
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40 CFR Part 60
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; Proposed Rule
Federal Register / Vol. 73, No. 114 / Thursday, June 12, 2008 /
Proposed Rules
[[Page 33642]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 60
[EPA-HQ-OAR-2005-0031; FRL-8576-2]
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: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to amend the new source performance standards
for electric utility steam generating units and industrial-commercial-
institutional steam generating units. On June 13, 2007, EPA promulgated
amendments to the standards for steam generating units. Subsequently,
EPA received a petition for reconsideration which it is granting to the
extent specified in the proposed action. EPA is proposing to amend
specific provisions in the standards for steam generating units, as
amended, to resolve issues and questions raised by the petitioner for
reconsideration, and to correct technical and editorial errors that
have been identified since promulgation. In addition, EPA is requesting
comment on the appropriate opacity standard for owners/operators of
affected facilities using a particulate matter continuous emissions
monitoring system to demonstrate compliance with the applicable PM
limit.
DATES: Comments. Comments must be received on or before July 28, 2008.
If anyone contacts EPA by June 23, 2008 requesting to speak at a public
hearing, EPA will hold a public hearing on June 27, 2008.
ADDRESSES: Comments. Submit your comments, identified by Docket ID No.
EPA-HQ-OAR-2005-0031, by one of the following methods:
https://www.regulations.gov. Follow the on-line
instructions for submitting comments.
E-mail: a-and-r-docket@epa.gov.
By Facsimile: (202) 566-1741.
Mail: Air and Radiation Docket, U.S. EPA, Mail Code 6102T,
1200 Pennsylvania Ave., NW., Washington, DC 20460. Please include a
total of two copies. In addition, please mail a copy of your comments
on the information collection provisions to the Office of Information
and Regulatory Affairs, Office of Management and Budget (OMB), Attn:
Desk Officer for EPA, 725 17th Street, NW., Washington, DC 20503. EPA
requests a separate copy also be sent to the contact person identified
below (see FOR FURTHER INFORMATION CONTACT).
Hand Delivery: EPA Docket Center, Docket ID Number EPA-HQ-
OAR-2005-0031, EPA West Building, 1301 Constitution Ave., NW., Room
3334, Washington, DC 20004. Such deliveries are accepted only during
the Docket's normal hours of operation, and special arrangements should
be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2005-0031. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through regulations.gov or e-
mail. The https://www.regulations.gov Web site is an ``anonymous
access'' system, which means EPA will not know your identity or contact
information unless you provide it in the body of your comment. If you
send an e-mail comment directly to EPA without going through https://
www.regulations.gov, your e-mail address will be automatically captured
and included as part of the comment that is placed in the public docket
and made available on the Internet. If you submit an electronic comment
through https://www.regulations.gov, EPA recommends that you include
your name and other contact information in the body of your comment as
well as with any disk or CD-ROM you submit. If EPA cannot read your
comment due to technical difficulties and cannot contact you for
clarification, EPA may not be able to consider your comment. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses. For additional
information about EPA's public docket visit the EPA Docket Center
homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the https://
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Air and Radiation
Docket EPA/DC, 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 and Radiation 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:
Regulated Entities. Entities potentially affected by this proposed
action include, but are not limited to, the following:
------------------------------------------------------------------------
Examples of regulated
Category NAICS \1\ 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 utility
steam generating
units located in
Indian Country.
[[Page 33643]]
Any industrial, commercial, or 211 Extractors of crude
institutional facility using 321 petroleum and natural
a steam generating unit as 322 gas.
defined in 60.40b or 60.40c. 325 Manufacturers of
324 lumber and wood
products.
Pulp and paper mills.
Chemical
manufacturers.
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 the
proposed rule. To determine whether your facility is regulated by the
proposed rule, you should examine the applicability criteria in Sec.
60.40a, Sec. 60.40b, or Sec. 60.40c of 40 CFR part 60. If you have
any questions regarding the applicability of the proposed rule to a
particular entity, contact the person listed in the preceding FOR
FURTHER INFORMATION CONTACT section.
WorldWide Web (WWW). Following the Administrator's signature, a
copy of the proposed amendments will be posted on the Technology
Transfer Network's (TTN) policy and guidance page for newly proposed or
promulgated rules at https://www.epa.gov/ttn/oarpg. The TTN provides
information and technology exchange in various areas of air pollution
control.
Public Hearing. If a public hearing is requested, it will be held
at 10 a.m. at the EPA Facility Complex in Research Triangle Park, North
Carolina or at an alternate site nearby. Contact Mr. Christian Fellner
at 919-541-4003 to request a hearing, to request to speak at a hearing,
to determine if a hearing will be held, or to determine the hearing
location.
Outline. The information presented in this preamble is organized as
follows:
I. Background
II. Proposed Amendments
A. Opacity Monitoring
B. Additional Proposed Amendments to Subpart D
C. Additional Proposed Amendments to Subpart Da
D. Additional Proposed Amendments to Subpart Db and Dc
III. Rationale for Proposed Amendments
A. Alternate Opacity Monitoring
B. Additional Proposed Amendments to Subpart Da
C. Additional Proposed Amendments to Subparts Db and Dc
IV. Opacity Monitoring for Facilities With PM CEMS
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paper 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
I. Background
New source performance standards (NSPS) implement Clean Air Act
(CAA) section 111(b) and are issued for categories of sources which
have been identified as causing, or contributing significantly to, air
pollution which may reasonably be anticipated to endanger public health
or welfare. The primary purpose of the NSPS are to help States attain
and maintain ambient air quality by ensuring that the best demonstrated
emission control technologies are installed as industrial
infrastructure is modernized. Since 1970, the NSPS have been successful
in achieving long-term emissions reductions in numerous industries by
assuring cost-effective controls are installed on new, reconstructed,
and modified sources.
CAA section 111 requires that NSPS reflect the degree of emission
limitation achievable through application of the best system of
emissions reductions which (taking into consideration the cost of
achieving such emissions reductions, any non-air quality health and
environmental impact, and energy requirements) the Administrator
determines has been adequately demonstrated. This level of control is
commonly referred to as best demonstrated technology (BDT). CAA section
111(b)(1)(B) requires the EPA to periodically review and revise the
standards of performance, as necessary, to reflect improvements in
methods for reducing emissions.
We promulgated amendments to the new source performance standards
for steam generating units (40 CFR part 60, subparts D, Da, Db, and Dc)
on June 13, 2007 (72 FR 32710). The amendments added compliance
alternatives for owners and operators of certain affected sources,
revised certain recordkeeping and reporting requirements, corrected
technical and editorial errors, and updated the grammatical style of
the four subparts to be more consistent across all four steam
generating unit NSPS.
A petition for reconsideration of the amendments was filed by the
Coke Oven Environmental Task Force (COETF), and we have decided to
grant reconsideration of the amendments to the extent specified in the
proposed rule. The amendments proposed by this action address specific
issues for which the petitioners requested reconsideration.
As part of this action, we are also proposing to specify opacity
monitoring requirements for owners/operators of affected facilities
that are subject to an opacity limit, but are not required to use a
continuous opacity monitor system (COMS). In addition, we are proposing
to amend other rule language to correct technical omissions,
typographical errors, cross-reference errors, grammatical errors, and
various other issues that have been identified since promulgation of
the previous amendments. The proposed amendments would not
significantly change our original projections for the rule's compliance
costs, environmental benefits, burden on industry, or the number of
affected facilities.
[[Page 33644]]
II. Proposed Amendments
A. Opacity Monitoring
We are proposing multiple options to monitor opacity for owners/
operators of affected facilities that are subject to an opacity limit,
but exempt from the COMS requirement. Under the first option, the
owner/operator conducts an annual EPA Method 9 opacity performance test
on each affected facility to demonstrate compliance with the applicable
opacity limit. A second option is for the owner/operator to use annual
EPA Method 22 observations in lieu of Method 9 observations to
demonstrate that the sum of occurrences of any visible emissions is not
in excess of 5 percent of the observation period. As a third option, we
are proposing the use of a digital photographic technique for detecting
visible emissions, as an explicit alternative to Method 22
observations. This proposed rule references an EPA preliminary method
entitled ``Determination of Visible Emission Opacity from Stationary
Sources Using Computer-Based Photographic Analysis Systems'' found at
https://www.epa.gov/tnn/emc/prelim/pre-008.pdf. For this third option,
the facility owner/operator would prepare a site-specific monitoring
plan based on this technology for approval. Observations using either
Method 22 or the digital photographic technique demonstrating that the
presence of visible emissions is less than 5 percent of the observation
period would be sufficient to demonstrate compliance with the opacity
limit. However, if either the Method 22 observation or the digital
photographic technique shows the presence of visible emissions in
excess of 5 percent of the observation period, then the owner/operator
would be required to conduct a Method 9 performance test within 24
hours to demonstrate compliance with the opacity limit.
We are also proposing to require owners/operators of affected
facilities that elect to use PM CEMS to measure both the filterable and
condensable particulate matter emissions and to take Method 9 opacity
readings during the initial PM CEMS calibration and ongoing correlation
testing and to electronically report those results.
B. Additional Proposed Amendments to Subpart D
We are proposing to exempt owners/operators of affected facilities
subject to subpart D that burn 500 part per million (ppm) or less
sulfur distillate oil from the requirement to install a COMS.
C. Additional Proposed Amendments to Subpart Da
We are proposing several additional amendments to subpart Da.
First, we are proposing to exempt from the requirement to install a
COMS owners/operators of affected facilities subject to subpart Da that
burn 500 ppm or less sulfur distillate oil. Second, we are proposing to
add a provision to postpone PM performance testing for owners/operators
of affected facilities that are not operating at the time a PM
performance test is required to be conducted. The PM performance test
would not be required until after the affected facility recommences
operation. Finally, we are proposing to add a provision requiring that
owners/operators of an affected facility constructed after February 28,
2005 with a wet scrubber for which the owner/operator elects to use the
opacity baseline approach to monitor the performance of their primary
PM control device, to maintain the liquid-to-gas flow rate at 90
percent or higher of the ratio measured during the most recent PM
performance test.
D. Additional Proposed Amendments to Subpart Db
We are proposing several amendments to subpart Db. First, since
synthetic natural gas derived from coal has uncontrolled emissions
similar to those of natural gas, we are proposing that synthetic
natural gas derived from coal be considered natural gas instead of coal
under the rule. Similarly, since diesel fuel has emissions similar to
distillate oil, we are proposing to include diesel fuel in the
definition of distillate oil. Second, we are proposing to amend the
definition of potential sulfur dioxide emission rate. This will clarify
that owners/operators of boilers burning gasified coal and oil that has
been desulfurized prior to combustion are able to claim credit for
pretreatment reductions when using the fuel-based compliance
alternatives. Third, we are proposing to amend the definition of steam
generating unit to clarify that all water heaters, regardless of the
mechanism used to heat the water, are covered by the NSPS. Fourth, we
are proposing to change the definition of very low sulfur oil from 0.30
weight percent sulfur to 0.50 weight percent sulfur for owners/
operators of affected facilities built after February 28, 2005, that
are located in noncontinental areas. Finally, we are proposing to allow
fuel blending to achieve the optional numerical sulfur dioxide
(SO2) limit.
We are proposing to make several amendments primarily impacting
owner/operators of boilers burning coke oven gas (COG). First, we are
proposing to align the regulatory test with the intent of the
amendments published June 13, 2007 (72 FR 32710) and extend the 30-day
SO2 limit maintenance exemption to owners/operators of COG-
fired boilers constructed prior to February 28, 2005 to include
maintenance of all SO2 control technologies in the
exemption, and to require reporting of what maintenance was performed
during the control device outage. We are also proposing that owners/
operators of affected facilities burning gasified coal receive the same
nitrogen oxide (NOX) monitoring options as owners/operators
of affected facilities burning natural gas. If adopted, this amendment
would provide owners/operators of affected facilities burning gasified
coal the option to develop a site-specific monitoring plan as an
alternative to using a NOX CEMS to monitor NOX
emissions.
E. Additional Proposed Amendments to Subpart Dc
We are proposing several amendments to subpart Dc. First, since
synthetic natural gas derived from coal has uncontrolled emissions
similar to those of natural gas, we are proposing that synthetic
natural gas derived from coal be considered natural gas instead of
coal. Similarly, since diesel fuel has emissions similar to those of
distillate oil, we are proposing to include diesel fuel in the
definition of distillate oil. Second, we are proposing to amend the
definition of steam generating unit to clarify that all water heaters,
regardless of the mechanism used to heat the water, are covered by the
NSPS. Finally, we are proposing to allow fuel blending to achieve the
optional numerical SO2 limit.
III. Rationale for Proposed Amendments
A. Alternate Opacity Monitoring
The amendments to the new source performance standards for steam
generating units promulgated on June 13, 2007 (72 FR 32710) eliminated
the requirement to install and properly operate a COMS, but not the
opacity standard, for owners/operators of certain affected facilities.
Those affected facilities include any steam generating unit using a PM
CEMS to demonstrate compliance with the applicable PM limit, oil-fired
steam generating units with a carbon monoxide CEMS, steam generating
units firing 500 ppm sulfur distillate oil or less (subparts Db and Dc
only), and owners/operators monitoring
[[Page 33645]]
opacity emissions under a site-specific plan approved by the permitting
authority (subparts Db and Dc only). We intended in promulgating the
previous amendments to provide the COMS exemption to owners/operators
of steam generating units firing 500 ppm sulfur distillate oil or less
across all of the subparts. However, we only added the regulatory
language to subparts Db and Dc. The proposed amendments will implement
the intent of the previous rulemaking by adding the language to
subparts D and Da.
The previous amendments did not specify the type and frequency of
alternate opacity monitoring for affected facilities that do not
demonstrate compliance with the opacity limit using a COMS. Without
adding specific requirements, it would be up to the permitting
authority to determine the proper level of monitoring. Since the COMS
exemption is only available to owner/operators of facilities
continuously monitoring parameters indicative of opacity (i.e., oil-
fired facilities with CO CEMS) or burning fuels with inherently low
opacity (i.e., 500 ppm sulfur distillate oil-fired facilities), we are
proposing to require opacity observations be done only every 12 months.
However, this does not prevent the permitting authority, or any
qualified individual, from performing Method 9 observation at any time
to determine excess opacity. While Method 9 remains the most reliable
means of determining compliance with an applicable opacity limit, we
are including Method 22 as an alternative to Method 9 since it requires
an observer, but not necessarily a certified Method 9 observer. This
option is likely to lower the compliance burden, since an uncertified
observer is able to monitor the affected facility for any visible
emissions (i.e., not zero). For sources with multiple stacks, the use
of a digital camera system would also reduce compliance costs, while
still providing equivalent protection for the environment.
Due to the potential emissions from steam generating units,
especially utility size facilities, we are specifically requesting
comment on whether the frequency of the opacity observations should be
increased and are considering two alternatives for the final rule. The
first would increase the frequency of performance testing and require
that Method 9 performance tests be completed once each calendar month
or once each calendar quarter. The second alternate approach we are
considering would require the owner/operator to perform either daily or
weekly Method 22 (or digital photographic technique) brief observations
(i.e., 5 to 15 minutes). If any visible emissions are detected, the
owner/operator would be required to conduct a longer (i.e., at least 1
hour) observation to determine if the sum of the time visible emissions
are present is less than 5 percent of the observation period. If the
visible emissions are in excess of 5 percent of the observation period,
then a Method 9 performance test would be required within 24 hours. The
benefit of the frequent, but brief, Method 22 approach is that it
provides more assurance than the once a year approach that the facility
is operating properly, but it still keeps the compliance burden
relatively low.
B. Additional Proposed Amendments to Subpart Da
We are proposing to delay the required PM performance test for
facilities that are not operating at the time such a test is otherwise
required because we have concluded that it is not beneficial to the
environment or appropriate to require a facility to operate just to
conduct a performance test. Also, in the June 13, 2007 rulemaking (72
FR 32710), we intended to include the requirement that owners/operators
of an affected facility constructed after February 28, 2005 that
employs a wet scrubber who choose to use a baseline opacity level to
monitor PM control device performance maintain the liquid to gas ratio
of the scrubber that was used during the most recent performance test.
Since scrubbers can potentially impact PM emissions, we have concluded
that it is necessary that the liquid to gas ratio be maintained at the
same or higher level as during the performance test as part of the
requirement to demonstrate continuous compliance with the PM limit.
This provision is presently included in the requirements for owners/
operators using a predictive electrostatic precipitator (ESP) model to
monitor PM control device performance, and the proposed amendments
update the regulatory text to reflect the intent of the original
rulemaking.
C. Additional Proposed Amendments to Subparts Db and Dc
The intent of the alternate numerical SO2 limit of 0.20
lb SO2/MMBtu added in the amendments published on February
27, 2006 (71 FR 9866) was to provide flexibility to owners/operators of
steam generating units burning fuels with inherently low sulfur
contents. We are proposing to clarify that fuel blending with low
sulfur fuels (i.e. natural gas) can be done to achieve the optional
numerical SO2 limit. The use of fuel blending decreases
compliance costs for facilities. If a facility gets a single delivery
of fuel with higher than expected sulfur content, the facility owner/
operator can blend in low sulfur fuels to achieve the standard.
The proposal also clarifies that the term steam generating unit
includes units which heat water regardless of whether the water is
heated directly, indirectly, or as a heat transfer medium. The
preambles to the final subpart Db rulemakings (November 25, 1986, 51 FR
42768 and 42772) and December 16, 1987 (52 FR 47826) were clear about
our intent to include facilities which produce hot water without
subsequently converting the water to steam in the definition of steam
generating unit. Because there continues to be questions as to whether
the definition of steam generating unit includes direct contact water
heaters, we are taking this opportunity to confirm that ``steam
generating unit'' includes any unit that combusts fuel and heats water,
and does not categorically exclude direct contact water heaters. This
clarification is not meant to reverse source-specific applicability
determinations that were issued prior to today. We are also reaffirming
that fuel combustion units which function as process heaters are not
covered as steam generating units if their primary purpose is to heat a
fluid in order to initiate or promote a chemical reaction in which the
fluid itself is a reactant or catalyst. The heating of water to act as
a heat transfer medium for vaporizing liquid natural gas, for example,
would not generally meet the definition of a process heater.
The proposed amendments addressing steam generating units located
in noncontinental areas that burn distillate oil or residual oil is
based on the fact that oil containing 0.30 weight percent or less
sulfur is not always readily available to owners/operators of such
units, but that 0.50 weight percent sulfur distillate oil and residual
oil are generally available. It was not the intent of the amendments
published on February 27, 2006 (71 FR 9866) to require owners/operators
of oil-fired steam generating units located in noncontinental areas to
incur high fuel transportation costs or to install post combustion
controls on oil-fired boilers. The proposed amendments to the
definition of very low sulfur oil and the corresponding low sulfur oil
PM exemption and SO2 limit exemptions would allow owner/
operators of oil-fired steam generating units located in noncontinental
areas to demonstrate compliance with both limits using fuel receipts.
We are proposing that gasified coal (including COG) have the same
NOX
[[Page 33646]]
monitoring option as natural gas, distillate oil, and low nitrogen
content residual oil since gasified coal has uncontrolled
NOX emissions similar to those of natural gas. Even though
COG is a byproduct gas and not generated for the purposes of creating
useful heat, it is considered coal for the purposes of subpart Db. In
addition, even though the chemical compositions of COG and gasified
coal that is generated for the purposes of creating useful heat are
different, both have similar uncontrolled NOX emission
rates.
Because of the specific characteristics of the steel industry, the
current regulations allow a 30-day exceedance per year from the
SO2 emission limit for steam generating units constructed
after February 28, 2005 that burn COG exclusively or in combination
with other gaseous fuels or distillate oil. COG desulfurization
facilities regardless of when the steam generating units they serve
were constructed require periodic maintenance, but the coking process
continues during this time, and it is cost prohibitive to store the
COG. Coke-making facilities would either have to install a second
desulfurization unit or flare the COG and burn natural gas during the
maintenance period. Of these two options, the least cost option would
be to flare the COG and use natural gas during the annual maintenance.
This would result in both increased cost to the steel industry and
increased NOX emissions without achieving any reductions in
SO2. We are, therefore, proposing to expand this exemption
to owners/operators of COG-fired boilers constructed prior to February
28, 2005 and to the use of post-combustion controls since both pre- and
post-combustion controls require maintenance. We are also proposing to
add a reporting requirement to assure that any SO2
exceedances are due to valid maintenance periods.
IV. Opacity Monitoring for Facilities With PM CEMS
There are several conditions that result in opacity from steam
generating units. These include emissions of PM, NOX, and
reactions of stack gases in the atmosphere. However, opacity from
NOX emissions is rare and only occurs at high NOX
emissions rates. All modern steam generating units have inherent
NOX emissions rates below the level that would result in
opacity emissions. Therefore, for modern steam generating units, the
primary causes of opacity are PM and reactions of stack gases that
occur after the gases are discharged to the atmosphere. PM CEMS detect
solid or liquid PM at the stack conditions, and COMS detect anything
that blocks light at the stack conditions. Since PM CEMS measure
filterable PM (PM that is either in a solid or liquid state at the
stack conditions) and COMS measure opaque material that can be used as
a surrogate for particulate matter, we concluded in a previous
rulemaking (71 FR 9866) that it is appropriate for owners/operators of
affected facilities who use a PM CEMS (to demonstrate compliance with
the applicable PM limit) to eliminate the use of COMS. However, the
opacity standard itself was not eliminated, and owners/operators of
facilities who elect not to install PM CEMS are required to continue to
use COMS. Furthermore, it is possible that an owner/operator of an
affected facility could be in compliance with the opacity limit in the
stack (i.e., COMS measurements), but that a Method 9 observation could
detect plume opacity violations.
Since opacity data has been used as a surrogate for PM emissions
\1\ and since PM CEMS give a more direct continuous measurement of the
primary pollutant of interest causing opacity at steam generating units
and provides data in units of the PM standard, we are requesting
comment on if eliminating the opacity standard altogether for owner/
operators using PM CEMS would be appropriate. However, neither a COMS
nor a PM CEMS \2\ detects condensable PM (i.e., PM that is in the
gaseous state at the stack conditions but that will condense to form
solid or liquid particulate matter at atmospheric conditions).
Therefore, if we were to adopt this option and eliminate the opacity
requirement for affected facilities with PM CEMS, we are proposing to
require owners/operators of an affected facility with a PM CEMS to
measure and electronically report filterable and condensable PM along
with Method 9 opacity data (Method 9 observations of the plume opacity
may detect the presence of condensable PM) during the initial and
ongoing calibration of the PM CEMS. With sufficient data, we will be
able to determine if a relationship exists between filterable and
condensable PM and opacity and to establish direct or parametric
monitoring approaches for condensable PM, including those relying on
techniques other than opacity, and an appropriate condensable PM limit.
---------------------------------------------------------------------------
\1\ Opacity is also used as an indicator of control device
operation and proper maintenance.
\2\ New PM CEMS are being developed that may measure condensable
PM.
---------------------------------------------------------------------------
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
This action is not a ``significant regulatory action'' under the
terms of Executive Order (EO) 12866 (58 FR 51735, October 4, 1993) and
is, therefore, not subject to review under the EO. EPA has concluded
that the amendments will not change the costs or benefits of the rule.
However, EPA is requesting additional comments on the issue.
B. Paperwork Reduction Act
This action does not impose any new information collection burden.
The proposed amendments result in no changes to the information
collection requirements of the existing standards of performance and
would 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 has
previously approved the information collection requirements contained
in the existing regulations (40 CFR part 60, subparts Da, Db, and Dc)
under the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et
seq., at the time the standards were promulgated on June 11, 1979 (40
CFR part 60, subpart Da, 44 FR 33580), November 25, 1986 (40 CFR part
60, subpart Db, 51 FR 42768), and September 12, 1990 (40 CFR part 60,
subpart Dc, 55 FR 37674). OMB assigned OMB control numbers 2060-0023
for 40 CFR part 60, subpart Da, 2060-0072 for 40 CFR part 60, subpart
Db, and 2060-0202 for 40 CFR part 60, subpart Dc. The 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 this rule on small
entities, small entity is defined as: (1) A small business as defined
by the Small Business Administration's regulations at 13 CFR
[[Page 33647]]
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 proposed rule on
small entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities. This
proposed rule will not impose any requirements on small entities.
We continue to be interested in the potential impacts of the
proposed rule on small entities and welcome comments on issues related
to such impacts.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Public
Law 104-4, establishes requirements for Federal agencies to assess the
effects of their regulatory actions on State, local, and tribal
governments and the private sector. Under section 202 of the UMRA, EPA
generally must prepare a written statement, including a cost-benefit
analysis, for proposed and final rules with ``Federal mandates'' that
may result in expenditures to State, local, and tribal governments, in
the aggregate, or to the private sector, of $100 million or more in any
one year. Before promulgating an EPA rule for which a written statement
is needed, section 205 of the UMRA generally requires EPA to identify
and consider a reasonable number of regulatory alternatives and adopt
the least costly, most cost-effective or least burdensome alternative
that achieves the objectives of the rule. The provisions of section 205
do not apply when they are inconsistent with applicable law. Moreover,
section 205 allows EPA to adopt an alternative other than the least
costly, most cost effective or least burdensome alternative if the
Administrator publishes with the final rule an explanation why that
alternative was not adopted. Before EPA establishes any regulatory
requirements that may significantly or uniquely affect small
governments, including tribal governments, it must have developed under
section 203 of the UMRA a small government agency plan. The plan must
provide for notifying potentially affected small governments, enabling
officials of affected small governments to have meaningful and timely
input in the development of EPA regulatory proposals with significant
Federal intergovernmental mandates, and informing, educating, and
advising small governments on compliance with the regulatory
requirements.
EPA has determined that this rule does not contain a Federal
mandate that may result in expenditures of $100 million or more for
State, local, and tribal governments, in the aggregate, or the private
sector in any one year. Thus, this rule is not subject to the
requirements of section 202 and 205 of the UMRA. In addition, EPA
determined that this rule contains no regulatory requirements that
might significantly or uniquely affect small governments because the
burden is small and the regulation does not unfairly apply to small
governments. Therefore, this rule is not subject to the requirements of
section 203 of the UMRA.
E. Executive Order 13132: Federalism
Executive Order (EO) 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 EO 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 proposed 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 EO 13132. These proposed amendments will not impose
substantial direct compliance costs on State or local governments; they
will not preempt State law. Thus, EO 13132 does not apply to this rule.
In the spirit of EO 13132, and consistent with EPA policy to promote
communications between EPA and State and local governments, EPA
specifically solicits comment on this proposed rule from State and
local officials.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
Executive Order 13175, entitled ``Consultation and Coordination
with Indian Tribal Governments'' (65 FR 67249, November 9, 2000),
requires EPA to develop an accountable process to ensure ``meaningful
and timely input by tribal officials in the development of regulatory
policies that have tribal implications.'' This proposed rule does not
have tribal implications, as specified in EO 13175. Thus, EO 13175 does
not apply to this rule. EPA specifically solicits additional comment on
this proposed rule from tribal officials.
G. Executive Order 13045: Protection of Children From Environmental
Health and Safety Risks
EPA interprets EO 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 EO has the
potential to influence the regulation. This proposed rule is not
subject to EO 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 rule is not subject to Executive Order 13211, ``Actions
Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use'' (66 FR 28355 (May 22, 2001)) because it is not a
significant regulatory action under Executive Order 12866.
I. National Technology Transfer Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA''), Public Law No. 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 proposed rulemaking involves technical standards. EPA proposes
to use ASTM D975-08, ``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.
The 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.
[[Page 33648]]
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. EPA welcomes comments on this aspect of the proposed
rulemaking and, specifically, invites the public to identify
potentially-applicable voluntary consensus standards and to explain why
such standards should be used in this proposed action.
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 proposed rule will not have
disproportionately high adverse human health or environmental effects
on minority or low-income populations because it increases the level of
environmental protection for all affected populations without having
any disproportionately high adverse human health or environmental
effects on any populations, including any minority or low-income
population.
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: May 30, 2008.
Stephen L. Johnson,
Administrator.
For the reasons stated in the preamble, title 40, chapter I, part
60, of the Code of the Federal Regulations is proposed to be 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:
Sec. 60.17 Incorporations by Reference.
* * * * *
(17) ASTM D975-08, Standard Specification for Diesel Fuel Oils, IBR
approved for Sec. Sec. 60.41(b) of subpart Db of this part and 60.41c
of subpart Dc of this part.
* * * * *
Subpart D--[Amended]
3. 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.
* * * * *
4. Section 60.45 is amended to read as follows:
a. By revising paragraph (b)(1) and adding new paragraph (b)(7);
and
b. By revising paragraphs (g)(2),(g)(3), and (g)(4).
Sec. 60.45 Emissions and fuel monitoring.
* * * * *
(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.
* * * * *
(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
CEMS for measuring opacity 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 comply with either paragraphs (b)(7)(i), (b)(7)(ii), or
(b)(7)(iii) of this section.
(i) 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. The Method 9 observations
must be completed, at a minimum, every 12 months; or
(ii) Conduct a series of three 1-hour observations (during normal
operation) using Method 22 of Appendix A-7 of this part at the affected
facility 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., 9 minutes per 3-hour period). The Method 22 observations must be
completed, at a minimum, every 12 months. If the sum of the occurrences
of visible emissions in excess of 5 percent of the observation period,
then the owner or operator shall conduct a performance test within 24
hours according to the requirements in Sec. 60.46(a)(3); or
(iii) Monitor opacity using a digital opacity compliance system
according to a site-specific monitoring plan approved by the
Administrator. The observations should include at least one digital
image every 15 seconds for three separate 1-hour periods (during normal
operation) every 12 months. An approvable monitoring plan should
include a demonstration that the occurrences of visible emissions are
not in excess of 5 percent of the observation period (i.e., 36
observations per 3-hour period). 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. If the sum of the
occurrences of any visible emissions is in excess of 5 percent of the
observation period, then the owner or operator shall conduct a new
performance test within
[[Page 33649]]
24 hours according to the requirements in Sec. 60.46(a)(3).
* * * * *
(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
under 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 under 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 under 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 under 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 under Sec.
60.42. Affected facilities using PM CEMS in lieu of a CEMS for
monitoring opacity emissions must follow the most current applicable
compliance and monitoring provisions in Sec. Sec. 60.48Da and 60.49Da
of subpart Da of this part.
5. Section 60.46 is amended by revising paragraph (b)(2)
introductory text to read as follows:
Sec. 60.46 Test methods and procedures.
* * * * *
(b) * * *
(2) Method 5 of appendix A-3 of this part shall be used to
determine PM concentration (C) at affected facilities without wet flue-
gas-desulfurization (FGD) systems and Method 5B of appendix A-3 of this
part shall be used to determine the PM concentration (C) after FGD
systems. 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 2.1 and 2.3 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]
6. Section 60.40Da is amended by revising paragraph (b)(4) to read
as follows:
Sec. 60.40Da Applicability and designation of affected facility.
* * * * *
(b) * * *
(4) Heat recovery steam generators that are associated with
combined cycle gas turbines that meet the applicability requirements of
subpart KKKK of this part are not subject to this part. This subpart
will continue to apply to all other electric utility combined cycle gas
turbines that are capable of combusting more than 73 MW (250 MMBtu/hr)
heat input of fossil fuel in the heat recovery steam generator. If the
heat recovery steam generator is subject to this subpart and the
stationary combustion turbine is subject to either subpart GG or KKKK
of this part, only emissions resulting from combustion of fuels in the
steam-generating unit are subject to this subpart. (The stationary
combustion turbine emissions are subject to subpart GG or KKKK, as
applicable, of this part).
* * * * *
7. Section 60.41Da is amended in paragraph (c) by revising the
definitions of ``Gross output,'' ``Petroleum,'' and ``Potential
combustion concentration'' to read as follows:
Sec. 60.41Da Definitions.
* * * * *
(c) * * *
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).
* * * * *
Petroleum means crude oil or a fuel derived from crude oil,
including, but not limited to, distillate oil, residual oil, and
petroleum coke.
Potential combustion concentration means the theoretical emissions
(nanograms per joule (ng/J), lb/MMBtu heat input) that would result
from combustion of a fuel in an uncleaned state without emission
control systems and:
* * * * *
8. Section 60.48Da is amended to read as follows:
a. By revising paragraph (n);
b. By revising paragraphs (o) introductory text, (o)(1), (o)(2)(ii)
introductory text, (o)(2)(iii), (o)(2)(iv), (o)(2)(vi), (o)(3)(i),
(o)(3)(iii), and (o)(5); and
c. By adding paragraph (q).
Sec. 60.48Da Compliance provisions.
* * * * *
(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 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 and Sec. 60.49Da(a)(2), 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
[[Page 33650]]
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. An affected facility that has not operated
for 2 months prior to the due date of a performance test is not
required to perform the subsequent performance test until 60 days after
the next boiler operating day.
(2) * * *
(ii) You must comply with the quality assurance requirements in
paragraphs (o)(2)(ii)(A) through (E) of this section.
* * * * *
(iii) During each performance test conducted according to paragraph
(o)(1) of this section, you must establish an opacity baseline level.
The value of the opacity baseline level is determined by averaging all
of the 6-minute average opacity values (reported to the nearest 0.1
percent opacity) from the COMS measurements recorded during each of the
test run intervals conducted for the performance test, and then adding
2.5 percent opacity to your calculated average opacity value for all of
the test runs. 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 alone or in
combination with another PM control device to comply with the PM
emissions limit, the daily average liquid-to-gas flow rate for the wet
scrubber must be maintained at least at 90 percent of average ratio
measured during all test run intervals for the performance test
conducted according to paragraph (o)(1) of this section.
* * * * *
(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 daily average liquid-to-gas flow rate for
the wet scrubber must be maintained at least at 90 percent of average
ratio measured during all test run intervals for the performance test
conducted according to paragraph (o)(1) of this section.
* * * * *
(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. If the values for one or
more of the model parameters exceed the applicable baseline levels
determined according to your approved site-specific monitoring plan,
you must initiate investigation of the relevant equipment and control
systems within 24 hours of the first discovery of a model