Transition to New or Revised Particulate Matter (PM); National Ambient Air Quality Standards (NAAQS), 6718-6729 [E6-1798]
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6718
Federal Register / Vol. 71, No. 27 / Thursday, February 9, 2006 / Proposed Rules
076°31′05.2″ W thence to the north
shoreline at latitude 39°00′54.7″ N,
longitude 076°30′44.8″ W, this line is
approximately 1300 yards northwest of
the U.S. 50 fixed highway bridge. The
regulated area is bounded to the
southeast by a line drawn from the
Naval Academy Light at latitude
38°58′39.5″ N, longitude 076°28′49″ W
thence southeast to a point 700 yards
east of Chinks Point, MD at latitude
38°58′1.9″ N, longitude 076°28′1.7″ W
thence northeast to Greenbury Point at
latitude 38°58′29″ N, longitude
076°27′16″ W. All coordinates reference
Datum NAD 1983.
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(c) Enforcement period. (1) This
section will be enforced during, and 30
minutes before each of the following
annual events:
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*
*
*
§ 100.518
[Suspended]
3. From March 1, 2006 through June
1, 2006, suspend § 100.518.
4. From March 1, 2006 through June
1, 2006, add temporary § 100.35–T06–
007 to read as follows:
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§ 100.35–T06–007, Severn River, College
Creek, Weems Creek and Carr Creek,
Annapolis, Maryland.
(a) Regulated area. (1) The regulated
area is established for the waters of the
Severn River from shoreline to
shoreline, bounded to the northwest by
a line drawn from the south shoreline at
latitude 39°00′38.9″ N, longitude
076°31′05.2″ W thence to the north
shoreline at latitude 39°00′54.7″ N,
longitude 076°30′44.8″ W, this line is
approximately 1300 yards northwest of
the U.S. 50 fixed highway bridge. The
regulated area is bounded to the
southeast by a line drawn from the
Naval Academy Light at latitude
38°58′39.5″ N, longitude 076°28′49″ W
thence southeast to a point 700 yards
east of Chinks Point, MD at latitude
38°58′1.9″ N, longitude 076°28′1.7″ W
thence northeast to Greenbury Point at
latitude 38°58′29″ N, longitude
076°27′16″ W. All coordinates reference
Datum NAD 1983.
(b) Definitions. (1) Coast Guard Patrol
Commander means a commissioned,
warrant, or petty officer of the Coast
Guard who has been designated by the
Commander, Coast Guard Sector
Hampton Roads.
(2) Official Patrol means any vessel
assigned or approved by Commander,
Coast Guard Sector Hampton Roads
with a commissioned, warrant, or petty
officer on board and displaying a Coast
Guard ensign.
(c) Special local regulations. (1)
Except for persons or vessels authorized
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by the Coast Guard Patrol Commander,
no person or vessel may enter or remain
in the regulated area.
(2) The operator of any vessel in the
immediate vicinity of the regulated area
shall:
(i) Stop the vessel immediately when
directed to do so by any Official Patrol
and then proceed only as directed.
(ii) All persons and vessels shall
comply with the instructions of the
Official Patrol.
(3) Any spectator vessel may anchor
outside of the regulated area specified in
paragraph (a)(1) of this section but may
not block a navigable channel.
(d) Enforcement period. (1) This
section will be enforced from 5 a.m. to
6 p.m. on those days and if the event’s
daily activities should conclude prior to
6 p.m., enforcement of this proposed
regulation may be terminated for that
day at the discretion of the Patrol
Commander. Enforcement will be
during, and 30 minutes before each of
the following annual events:
(i) Safety at Sea Seminar, April 1,
2006;
(ii) Naval Academy Crew Races,
March 25, April 15, April 22, April 23,
May 12 and May 28, 2006;
(iii) Blue Angels Air Show, May 23
and May 24, 2006.
(2) The Commander, Fifth Coast
Guard District will publish a notice in
the Fifth Coast Guard District Local
Notice to Mariners announcing the
specific event times.
(e) Effective period. This section is
effective from March 1, 2006 through
June 1, 2006.
Dated: January 23, 2006.
Larry L. Hereth,
Rear Admiral, U.S. Coast Guard, Commander,
Fifth Coast Guard District.
[FR Doc. E6–1738 Filed 2–8–06; 8:45 am]
BILLING CODE 4910–15–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 51
[EPA–HQ–OAR–2005–0175; FRL–8030–6]
Transition to New or Revised
Particulate Matter (PM); National
Ambient Air Quality Standards
(NAAQS)
Environmental Protection
Agency (EPA).
ACTION: Advance Notice of Proposed
Rulemaking (ANPR).
AGENCY:
SUMMARY: The EPA recently issued a
notice of proposed revisions to the
national ambient air quality standards
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(NAAQS) for particulate matter (PM).
EPA will take final action on the
proposal by September 27, 2006. This
notice provides advance notice of key
issues for consideration in the
development of potentially new or
revised policies and/or regulations to
implement revisions to the NAAQS for
PM recognizing that no final decision
has been made concerning whether or
how to revise the PM NAAQS. The EPA
is posing a number of questions related
to the transition from the current to
potentially revised PM2.5 standards, as
well as the transition from the current
PM10 standards to potentially new
PM10–2.5 standards. In this ANPR, EPA is
soliciting comment on the Agency’s
preferred approaches to revocation of
the 1997 PM2.5 standards once any new
2006 PM2.5 standards would be in place,
and also approaches to revocation of the
24-hour PM10 standard in areas where it
would remain after promulgation of any
new PM10–2.5 standards. The EPA is also
highlighting and providing preliminary
thinking on how to address some of the
key New Source Review (NSR) issues
related to the new PM10–2.5 standards,
and the transition from PM10 standards
to PM10–2.5 standards. Finally, EPA is
requesting comment on potential
timeframes for designations, attainment
demonstrations and State
Implementation Plan (SIP) submittals
and attainment dates for both any new
PM2.5 and PM10–2.5 standards.
DATES: Comments must be received on
or before April 10, 2006.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2005–0175, 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,
Attention Docket ID No. EPA–HQ–
OAR–2005–0175.
• Fax: Fax your comments to (202)
566–1741, Attention Docket ID. No.
EPA–HQ–OAR–2005–0175.
• Mail: Docket EPA–HQ–OAR–2005–
0175 Environmental Protection Agency,
Mail Code: 6102T, 1200 Pennsylvania
Ave., NW., Washington, DC, 20460.
Please include a total of two copies.
• Hand Delivery: Deliver your
comments to: Air Docket,
Environmental Protection Agency, 1301
Constitution Avenue, NW., Room B102,
Washington, DC 20004, Attention
Docket ID No. EPA–HQ–OAR–2005–
0175. Such deliveries are only accepted
during the Docket’s normal hours of
operation, and special arrangements
should be made for deliveries of boxed
information.
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Federal Register / Vol. 71, No. 27 / Thursday, February 9, 2006 / Proposed Rules
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2005–
0175. The 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 https://
www.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, EPA
recommends that you include your
name and other contact information in
the body of your comment 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
further information about EPA’s public
docket visit the EPA Docket Center
homepage at https://www.epa.gov/
epahome/dockets.htm. For additional
instruction on submitting a comment, go
to ‘‘What Should I Consider as I Prepare
My Comments for the EPA?’’ of the
SUPPLEMENTARY INFORMATION section of
this document.
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 EPA Docket Center, EPA/DC, EPA
West, Room B102, 1301 Constitution
Avenue, 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. A
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reasonable fee may be charged for
copying. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT: For
questions regarding PM implementation
issues, contact Ms. Barbara Driscoll,
U.S. Environmental Protection Agency,
Office of Air Quality Planning and
Standards, Mail Code C504–02,
Research Triangle Park, NC 27711,
phone number (919) 541–1051 or by email at: driscoll.barbara@epa.gov.
Regarding NSR issues, contact Raj Rao,
U.S. Environmental Protection Agency,
Office of Air Quality Planning and
Standards, Mail Code C339–03,
Research Triangle Park, NC 27711,
phone number (919) 541–5344 or by email at rao.raj@epa.gov.
SUPPLEMENTARY INFORMATION:
How Should I Submit CBI to the
Agency?
Do not submit information that you
consider to be CBI through https://
www.regulations.gov or e-mail. Clearly
mark the part or all of the information
that you claim to be CBI.
For CBI information in a disk or CD–
ROM that you mail to EPA, mark the
outside of the disk or CD–ROM as CBI
and then identify electronically within
the disk or CD–ROM the specific
information that is claimed as CBI. In
addition to one complete version of the
comment that includes information
claimed as CBI, a copy of the comment
that does not contain the information
claimed as CBI must be submitted for
inclusion in the public docket.
Information so marked will not be
disclosed except in accordance with
procedures set forth in 40 CFR part 2.
Send or deliver information identified
as CBI only to the following address:
Roberto Morales, U.S. EPA, Office of Air
Quality Planning and Standards, Mail
Code C404–02, Research Triangle Park,
NC 27711, telephone (919) 541–0880, email at morales.roberto@epa.gov,
Attention Docket ID No. EPA–HQ–
OAR–2005–0175.
What Should I Consider as I Prepare
My Comments for EPA?
You may find the following
suggestions helpful for preparing your
comments:
1. Explain your views as clearly as
possible.
2. Describe any assumptions that you
used.
3. Provide any technical information
and/or data you used that support your
views.
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4. If you estimate potential burden or
costs, explain how you arrived at your
estimate.
5. Provide specific examples to
illustrate your concerns.
6. Offer alternatives.
7. Make sure to submit your
comments by the comment period
deadline identified.
8. To ensure proper receipt by EPA,
identify the appropriate docket
identification number in the subject line
on the first page of your response. It
would also be helpful if you provided
the name, date, and Federal Register
citation related to your comments.
Table of Contents
I. What Actions Related to the PM NAAQS
Have Recently Been Proposed or Will
Soon Be Proposed Which Relate to This
Notice?
A. National Ambient Air Quality Standards
for Particulate Matter
B. Revisions to Ambient Air Monitoring
Regulations
C. Treatment of Data Influenced by
Exceptional Events
II. What Is EPA’S Strategy for Addressing
PM?
A. The State Implementation Plan (SIP)
System
B. National Rules
III. How Should EPA Implement the
Transition From the 1997 PM2.5 NAAQS
to Any New 2006 PM2.5 NAAQS?
A. What Is the Status of Areas Designated
Under the 1997 PM2.5 NAAQS?
B. How Might EPA Implement the
Transition from the 1997 PM2.5 NAAQS
to Any New 2006 PM2.5 NAAQS?
1. PM2.5 NAAQS Option 1
2. PM2.5 NAAQS Option 2
IV. What Are the Potential Timelines for
Implementation of Any New 2006 PM2.5
NAAQS?
A. How Would the Implementation
Schedules of the 1997 PM2.5 NAAQS and
Any New 2006 PM2.5 NAAQS Fit Together if
the Revised PM2.5 Standards Are More
Stringent Than the Current Standards?
B. What Is EPA’s Preferred Schedule for
Any New 2006 PM2.5 Designation
Process?
C. What Would the Schedule Be for
Attainment Demonstrations and SIP
Submittals for Any New 2006 PM2.5
Standards?
D. What Are Attainment Dates for Any
New 2006 PM2.5 Standards?
V. What Are the Potential Timelines for
Implementation of Any New PM10–2.5
NAAQS?
A. What Is a Potential Schedule for Any
New PM10–2.5 Designation Process?
B. What Is EPA’s Preferred Schedule for
Designations for any New PM10–2.5
Standards?
C. What Is EPA’s Preferred Schedule for
Attainment Demonstrations and SIP
Submittals for Any New PM10–2.5
Standards?
D. What Is EPA’s Preferred Schedule for
Attaining Any New PM10–2.5 Standards?
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VI. How Should EPA Implement the
Transition From the PM10 Standards to
Any New PM10–2.5 Standards?
A. What Is EPA’s Proposal for Revoking the
PM10 Standards?
B. What Should the Timing Be for
Revoking the 24-Hour PM10 Standard for
Those Areas Where the 24-Hour PM10
Standard Is Retained?
C. What Transition Issues Are Created by
Revoking the 24-Hour PM10 Standard in
Areas Where It is Currently Proposed to
be Retained and How Might They be
Addressed?
1. Control Measures
2. Transportation Conformity
3. General Conformity
4. New Source Review Program
VII. What Emissions Inventory Requirements
Should Apply Under Any New PM2.5
and PM10–2.5 NAAQS?
VIII. Statutory and Executive Order Reviews
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I. What Actions Related to the PM
NAAQS Have Recently Been Proposed
or Will Soon Be Proposed Which Relate
to This Notice?
This ANPR is intended to solicit input
into key issues related to the transition
to any new or revised NAAQS for PM.
The EPA has proposed two rulemakings,
the NAAQS for Particulate Matter;
Proposed Rule (71 FR 2620, January 17,
2006) and the Revisions to Ambient Air
Monitoring Regulations (71 FR 2710,
January 17, 2006), and will be proposing
another rulemaking, Treatment of Data
Influenced by Exceptional Events
(anticipated to be published by March
2006). These proposals are summarized
here to provide background for the
issues and questions raised in this
document. The EPA is not taking
comment on these actions here. Rather,
if you have comments, you should
submit them to the docket for the
proposed rulemaking to which they are
applicable, following the procedures
described in each proposal.
A. National Ambient Air Quality
Standards for Particulate Matter
On December 20, 2005, the
Administrator signed a notice proposing
revisions to the primary and secondary
NAAQS for PM, which was published
on January 17, 2006 (71 FR 2620). The
proposal can be found at: https://
www.epa.gov/oar/particlepollution/
actions.html. For the primary standards
for fine particles (particles generally less
than or equal to 2.5 micrometers (µm) in
diameter, or PM2.5), EPA proposed to
revise the level of the 24-hour PM2.5
standard from 65 micrograms per cubic
meter (µmg/m3) to 35 µg/m3, providing
increased protection against health
effects associated with short-term
exposure (including premature
mortality and increased hospital
admissions and emergency room visits)
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and to retain the level of the annual
PM2.5 standard at 15 µg/m3, continuing
protection against health effects
associated with long-term exposure
(including premature mortality and
development of chronic respiratory
disease). The EPA is also taking
comment on alternative NAAQS levels.
Additionally, EPA proposed to revise
the criteria for spatial averaging of
monitors for purposes of the annual
PM2.5 standard.
In addition, for the primary standards
for coarse particles generally less than
or equal to 10µm in diameter (PM10),
EPA proposed to revise the 24-hour
PM10 standard in part by establishing a
new indicator for thoracic coarse
particles (particles generally between
2.5 and 10µm in diameter, PM10–2.5),
qualified so as to include any ambient
mix of PM10–2.5 that is dominated by
resuspended dust from high-density
traffic on paved roads and PM generated
by industrial sources and construction
sources, and exclude any ambient mix
of PM10–2.5 that is dominated by rural
windblown dust and soils and PM
generated by agricultural and mining
sources. The EPA also proposed that
agricultural sources, mining sources and
other similar sources of crustal material
shall not be subject to control in
meeting the proposed standard. The
EPA proposed to set the new PM10–2.5
standard at a level of 70 µg/m3,
continuing to provide a generally
equivalent level of protection against
health effects associated with short-term
exposure (including hospital admissions
for cardiopulmonary diseases, increased
respiratory symptoms and possibly
premature mortality).
In addition, EPA proposed to revoke
the annual PM10 standard everywhere,
and the 24-hour PM10 standard
everywhere except in areas where there
is at least one monitor that is located in
an urbanized area1 with a minimum
population of 100,000 people and that
violates the 24-hour PM10 standard
based on the most recent 3 years of data.
This revocation of the PM10 standards
would become effective upon
promulgation of the PM10–2.5 NAAQS
(expected to be December 2006). In the
January 17, 2006, notice, the Agency
provided a specific list of areas where
the 24-hour PM10 standard would not be
1 As defined by the U.S. Bureau of the Census, an
urbanized area has ‘‘a minimum residential
population of at least 50,000 people’’ and generally
includes ‘‘core census block groups or blocks that
have a population density of at least 1,000 people
per square mile and surrounding census blocks that
have an overall density of at least 500 people per
square mile.’’ The Census Bureau notes that ‘‘under
certain conditions, less densely settled territory
may be part of each UA.’’ See https://
www.census.gov/geo/www/ua/ua_2k.html.
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revoked under the proposal based on
the most recent 3 years of data. EPA
proposed to revoke the 24-hour PM10
standard in all other areas. In addition,
EPA requested comment on whether the
24-hour PM10 standard should be
retained in additional areas that are
either urbanized areas with populations
less than 100,000 people or nonurbanized areas (i.e., populations less
than 50,000) but where the majority of
the ambient mix of PM10–2.5 is generated
by high density traffic on paved roads,
industrial sources, and construction
sources, and which have at least one
monitor that violated the 24-hour PM10
standard based on the most recent 3
years of data.
For the secondary PM standards, EPA
proposed to revise the current standards
by making them identical to the suite of
proposed primary standards for fine and
coarse particles.
B. Revisions to Ambient Air Monitoring
Regulations
At the same time EPA proposed
revisions to the PM NAAQS, EPA also
proposed Revisions to the Ambient Air
Monitoring Regulations (71 FR 2710,
January 17, 2006) for criteria pollutants
to support the proposed revisions to the
NAAQS. The proposal can be found at:
https://www.epa.gov/oar
/particlepollution/actions.html.
Included among the proposed PMrelated changes are new provisions to be
added to 40 CFR parts 53 and 58 which
address approval of monitoring methods
and PM10–2.5 monitoring requirements.
The added provisions in part 53 would
address approval of PM10–2.5 filter-based
Federal Reference Method (FRM)
samplers and both filter-based and
continuous Federal Equivalent Method
(FEM) monitors. Provisions in part 58
would provide the monitoring
requirements for a PM10–2.5 network,
including the minimum number of
monitors a State must deploy. In
addition, the proposal adds provisions
for the conditions under which a
PM10–2.5 monitor may be compared to
the PM10–2.5 NAAQS.
The proposal also amends a number
of existing provisions for PM2.5
monitoring, including changing the
criteria for FEM equivalency
determinations for continuous PM2.5
monitors. This should allow States to
operate continuous monitors at more
required monitoring sites, thereby
providing more robust data for the PM2.5
air quality program.
C. Treatment of Data Influenced by
Exceptional Events
The EPA will soon propose a rule to
govern the review and handling of air
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quality monitoring data influenced by
exceptional events. Section 319 of the
Clean Air Act (CAA) defines an event as
an exceptional event if the event affects
air quality; is not reasonably
controllable or preventable; is a natural
event, or an event caused by human
activity that is unlikely to recur at a
particular location; and is determined
by the Administrator to be an
exceptional event. The EPA will be
proposing procedures and criteria
related to the identification, evaluation,
interpretation and use of air quality
monitoring data related to the NAAQS
where State air quality agencies petition
EPA to exclude, in whole or in part, air
quality data that are directly affected by
exceptional events. Section 319 of the
CAA, as amended by section 6013 of the
Safe Accountable Flexible EfficientTransportation Equity Act (SAFE–TEA)
of 2005, requires EPA to publish a
proposed rule in the Federal Register,
no later than March 1, 2006.
uses to carry out its responsibilities
under the CAA, including the
attainment, maintenance, and
enforcement of the NAAQS. States use
the SIP process to identify the emissions
sources that contribute to the
nonattainment problem in a particular
area, and to select the emissions
reductions measures most appropriate
for that area, considering technical and
economic feasibility, and a variety of
local factors such as population
exposure, enforceability, and economic
impact. Under the CAA, SIPs must
ensure that areas reach attainment as
expeditiously as practicable. These
plans take into consideration emissions
reductions resulting from national
programs (such as mobile source
regulations, the acid rain program, or
maximum achievable control
technology (MACT) standards for air
toxics), as well as from State or local
programs not directly mandated under
the CAA.
II. What Is EPA’s Strategy for
Addressing PM?
Our overall strategy for achieving the
PM primary and secondary standards is
based on the structure outlined in the
CAA. The CAA outlines important roles
for State and Tribal governments and for
EPA in implementing NAAQS.
States have primary responsibility for
developing and implementing SIPs that
contain local and in-State measures
needed to achieve the air quality
standards in each area. We assist States
and Tribes by providing technical tools,
assistance and guidance, including
information on potential control
measures. The EPA recently issued a
Proposed rule to Implement the Fine
Particle NAAQS (70 FR 65984) to
support implementation of the 1997
PM2.5 NAAQS. In addition, we set
national emissions standards/limits for
some sources, such as new motor
vehicles, certain categories of major new
sources, and existing stationary sources
of toxic air pollutants, all of which may
obtain reductions in PM. Where upwind
sources (such as coal-fired power
plants) significantly contribute to
downwind problems in other States or
tribal areas, we can issue Federal
regulations to ensure that the upwind
States address these contributing
emissions (such as the Clean Air
Interstate Rule), or we can put in place
Federal regulations in situations where
the upwind States fail to address these
sources.
B. National Rules
As described in a recent EPA report,
The Particle Pollution Report: Current
Understanding of Air Quality and
Emissions through 2003,2 State and
Federal programs have made substantial
progress in reducing ambient
concentrations of PM10 and PM2.5. For
example, PM10 concentrations have
decreased 31 percent nationally since
1988. Regionally, PM10 concentrations
decreased most in areas with
historically higher concentrations—the
Northwest (39 percent decline), the
Southwest (33 percent decline), and
southern California (35 percent decline).
Direct emissions of PM10 have decreased
approximately 25 percent nationally
since 1988.
Programs aimed at reducing direct
emissions of particles have played an
important role in reducing PM10
concentrations, particularly in western
areas. Some examples of PM10 controls
include paving unpaved roads and
using best management practices for
agricultural sources of resuspended soil.
Of the 87 areas that were designated
nonattainment for PM10 in the early
1990’s, 64 now meet those standards. In
cities that have not attained the PM10
standards, the number of times the
standard is exceeded is down
significantly.
National programs that affect regional
emissions have contributed to lower
A. The State Implementation Plan (SIP)
System
A SIP is the compilation of
regulations and programs that a State
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2 Environmental Protection Agency (2004). The
Particle Pollution Report: Current Understanding of
Air Quality and Emissions through 2003. Office of
Air Quality Planning and Standards; Emissions,
Monitoring, and Analysis Division, Research
Triangle Park, NC 27711; report no. EPA–454–R–
04–002. December 2004.
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sulfate concentrations and,
consequently, to lower PM2.5
concentrations, particularly in the
Industrial Midwest and Southeast.
National ozone-reduction programs
designed to reduce emissions of volatile
organic compounds (VOCs) and
nitrogen oxides (NOX) also have helped
reduce carbon and nitrate particles, both
of which are components of PM2.5.
Power plant emissions of sulfur dioxide
dropped 33% from 1990 to 2003, largely
as a result of EPA’s Acid Rain Program.
Nationally, SO2 emissions have
declined 9 percent, NOX emissions have
declined 9 percent, and VOC emissions
have declined by 12 percent from 1999
to 2003. In eastern States affected by the
Acid Rain Program, sulfates decreased 7
percent over the same period.
Over the next 10 to 20 years, national
and regional regulations will make
major reductions in ambient PM2.5
levels. The Clean Air Interstate Rule
(CAIR) and the NOX SIP Call will reduce
SO2 and NOX emissions from electric
generating units and industrial boilers
across the eastern half of the U.S.,
regulations to implement the current
ambient air quality standards for PM2.5
will likely result in direct PM2.5 and
PM2.5 precursor controls in
nonattainment areas, and new national
mobile source regulations affecting offhighway diesel engines, highway
gasoline and diesel vehicles, and other
mobile sources will reduce emissions of
NOX, direct PM2.5, SO2, and VOCs. The
EPA estimates that these Federal
regulations for stationary and mobile
sources will cut SO2 emissions by 6
million tons annually in 2015 from 2001
levels. Emissions of NOX will be cut by
9 million tons annually in 2015 from
2001 levels. Emissions of VOCs will
drop by 3 million tons, and direct PM2.5
emissions will be cut by 200,000 tons in
2015, compared to 2001 levels.
III. How Should EPA Implement the
Transition From the 1997 PM2.5
NAAQS to Any New 2006 PM2.5
NAAQS?
A. What Is the Status of Areas
Designated Under the 1997 PM2.5
NAAQS?
On April 5, 2005, nonattainment
designations became final for 39
nonattainment areas. These areas were
designated based on air quality data
from 2001–2003 and 2002–2004.
Nationally, PM2.5 concentrations have
declined by 10 percent from 1999 to
2003. Generally, PM2.5 concentrations
have also declined the most in regions
with the highest concentrations—the
Southeast (20 percent decline), southern
California (16 percent decline), and the
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Midwest (9 percent decline)—with the
exception of the Northeast, where PM2.5
concentrations increased by 1%. Direct
emissions of PM2.5 have decreased by 5
percent nationally over the past 5 years.
Modeling done by EPA indicates that
by 2010, 18 of the 39 areas currently not
attaining the 1997 PM2.5 standards
should come into attainment of those
standards just based on regulatory
programs already in place, including
CAIR, the Clean Diesel Rules, and other
Federal measures. Four more PM2.5
areas are projected to attain the
standards by 2015 based on the
implementation of these programs. All
areas in the eastern U.S. will have lower
PM2.5 concentrations in 2015 relative to
present-day conditions. In most cases,
the predicted improvement in PM2.5
ranges from 10 percent to 20 percent.
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B. How Might EPA Implement the
Transition From the 1997 PM2.5 NAAQS
to Any New 2006 PM2.5 NAAQS?
The EPA has evaluated several
options for the transition from the 1997
PM2.5 standards to any new 2006 PM2.5
standards, and is elaborating on two
potential options. Should the Agency
decide to revise the current PM2.5
standards, then either of the following
two options would continue the
momentum and continuity of the
existing implementation program as
areas look to reduce ambient PM2.5
concentrations to meet the current and
revised PM2.5 NAAQS. Any suggested
alternatives to these approaches should
demonstrate how it will continue the
momentum and continuity of the
implementation program.
1. PM2.5 NAAQS Option 1
Option 1 recognizes that the only
proposed change to the 1997 annual
PM2.5 standard is a change in the
application of spatial averaging (71 FR
2620). Because the EPA believes that the
proposed change, if adopted, would not
be significant enough to require new
designations under section 107(d), we
are soliciting comment on whether it
would be appropriate to view this
revision as minor, thus not requiring a
designation process. Even though
section 107(d) calls for EPA to
commence the designation process for
‘‘any new or revised NAAQS,’’
exceptions could be made for revisions
to a NAAQS of a de minimis or
insignificant nature such that they
should not lead to the initiation of the
designation process and consequent
establishment of new SIP submission
and attainment deadlines. Option 1
would be considered only if EPA
finalized a revision to the annual PM2.5
standard that was of such a minor
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nature as the proposed revision. It
would not be available if EPA revised
the standard more substantially.
Following this path, EPA would
propose not to revoke the 1997 annual
PM2.5 standard, and would propose to
revoke the 1997 24-hour PM2.5 standard
1 year after designations are finalized
under any new 2006 PM2.5 standard.
With the exception of 2 areas in
California (South Coast Air Quality
District and San Joaquin Valley) all
areas designated as nonattainment for
PM2.5 were only violating the annual
standard. Under this path, new
nonattainment designations would only
be made for the areas which do not meet
any new 2006 24-hour PM2.5 standard.
Therefore, areas which are designated
nonattainment for the 1997 annual
PM2.5 standard would continue to
develop and implement their SIPs based
on a final implementation rule for the
PM2.5 NAAQS (proposed on November
1, 2005 at 70 FR 65984). Areas which
are newly designated nonattainment
under any new 24-hour PM2.5 standard
would submit a SIP by April 2013
following the proposed schedule in part
IV.C below. This approach would
maintain the momentum in the PM2.5
SIP development and implementation
program. It would also not require the
development and implementation of an
anti-backsliding rule to maintain
progress in the program, as no areas are
in nonattainment based solely on the
24-hour PM2.5 standard. Therefore
control measures would still be in place
under the approved PM2.5 SIPs.
2. PM2.5 NAAQS Option 2
Option 2 varies from Option 1 in that
EPA would revoke the 1997 annual and
24-hour PM2.5 standards 1 year after
designations under any new 2006 PM2.5
standards. This approach is similar to
that promulgated under the ozone
program (69 FR 23951, April 30, 2004)
for the revocation of the 1-hour ozone
standard one year after designations
under the 8-hour ozone standard.
Following this path, EPA would
develop and implement an ‘‘antibacksliding’’ rule to ensure that SIP
control measures developed and
adopted under the 1997 PM2.5 NAAQS
remained in place until SIPs could be
submitted and approved to meet any
new 2006 PM2.5 standards. In the antibacksliding rule, EPA would address
issues similar to those addressed in the
anti-backsliding rule adopted as part of
the transition from implementation of
the 1-hour ozone standard to the 8-hour
ozone standard including: (1) Which
planning and control requirements
should remain in effect; (2) effect of the
revised standards on the New Source
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Review (NSR) program; and (3) how the
transition would affect general and
transportation conformity programs. In
addressing some of these issues, EPA is
inclined to follow the precedent set by
the ozone program which required areas
in nonattainment with both the 1-hour
and 8-hour ozone NAAQS to maintain
mandatory control measures already in
place, and allowed such areas to revise
or remove discretionary control
measures following a section 110(l)
demonstration. In addition, such areas
would implement transportation
conformity and NSR based on their
designations for the revised standard
only, for the reasons explained in the
ozone anti-backsliding rule (69 FR
23954, April 30, 2004). The EPA invites
comment on these two options, and
solicits comments on any additional
options which would ensure a smooth
transition and continued improvement
in air quality.
IV. What Are the Potential Timelines
for Implementation of Any New 2006
PM2.5 NAAQS?
A. How Would the Implementation
Schedules of the 1997 PM2.5 NAAQS
and Any New 2006 PM2.5 NAAQS Fit
Together if the Revised PM2.5 Standards
Are More Stringent Than the Current
Standards?
Section 109(d)(1) of the CAA requires
a thorough review of the NAAQS, and
revisions if appropriate, at 5-year
intervals. Current requirements of the
CAA thus anticipate an overlap in
review and implementation of
standards. The EPA believes that for
planning purposes, when EPA revises a
standard as it has proposed to do, it is
beneficial for States to understand
control strategies that may be useful in
attaining any new 2006 PM2.5 standards
when developing control strategies for
the 1997 PM2.5 standards.
B. What Is EPA’s Preferred Schedule for
the Any New 2006 PM2.5 Designation
Process?
Under the terms of the consent decree
governing the review of the 1997 PM
NAAQS, EPA agreed that no later than
September 27, 2006, it would sign for
publication a notice of final rulemaking
concerning its review of the PM
NAAQS. The EPA expects that any new
2006 PM2.5 standards would be
published in the Federal Register
within 4 weeks, and become effective 60
days later probably in December 2006.
Timeframes below are outlined based on
this assumption. Section 107(d)(1) lays
out a schedule allowing States up to 1
year in which to make
recommendations to EPA for areas that
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might be designated as nonattainment
for any new PM2.5 standards. State
designation recommendations would
then be due by December 2007. Tribes
would also be encouraged, but not
required, to submit designation
recommendations to EPA for their
reservations or other areas under their
jurisdiction by December 2007.
These recommendations would be
based on 3 years of the most recent
monitoring data (e.g., 2004–2006). The
EPA(s evaluation of the existing PM2.5
monitoring network indicates that it is
adequate for designations under both
the proposed revised annual and
proposed revised 24-hour standards.
Depending on which revocation process
is selected for the 1997 PM2.5 NAAQS,
designations may be for the revised 24hour standard alone or both the annual
and 24-hour standards.
Following submittal of designation
recommendations by the States, EPA
would evaluate the recommendations
and make possible modifications.
Consistent with section 107, States
would be notified of these changes, and
would be allowed to make additional
comments on the proposed
designations. The EPA would issue final
PM2.5 designations under any new PM2.5
NAAQS no later than December 2009.
These designations would be effective
by April 2010. The CAA provides EPA
with up to 3 years to designate
nonattainment areas following
promulgation of a new or revised
NAAQS. The EPA anticipates that this
full time period may be necessary for a
variety of reasons as it has been in the
past, including evaluating more recent
data in order to determine appropriate
designation boundaries. This timeline
would allow States to look at 2006–2008
monitoring data and update their
recommendations to EPA if they choose
to do so based on the more recent data.
In addition, as was done for the 1997
PM2.5 NAAQS designations, we would
anticipate allowing a further update
based on 2007–2009 monitoring data,
and make designations effective in April
2010. Table 1 at the end of part IV(D)
provides a timeline showing the dates
that would result from such a
designation process. The EPA would
appreciate comments on this timeline
and other potential approaches.
C. What Would the Schedule Be for
Attainment Demonstrations and SIP
Submittals for Any New 2006 PM2.5
Standards?
Part D of title I of the CAA sets forth
the requirements for SIPs needed to
attain the NAAQS. Part D includes a
general subpart 1 which applies to all
NAAQS for which a specific subpart
does not exist. These provisions apply
to the PM2.5 standards and would apply
to any revised PM2.5 standards. The EPA
has currently proposed implementation
rules for PM2.5 (70 FR 65984) which,
when finalized, will govern any revised
standards.
Section 172(b) of the CAA requires
that at the time the Agency promulgates
nonattainment area designations, EPA
must also establish a schedule for States
to submit SIPs meeting the applicable
requirements of section 172(c) and
section 110(a)(2) of the CAA. Section
172(b) requires that such schedule allow
a State to submit its attainment
demonstration and SIP revision within
no more than 3 years of nonattainment
designation. Following the above
timeline (outlined in IV.B), if
nonattainment area designations
become effective in April 2010, and EPA
allows the maximum time for SIP
6723
submissions, then attainment
demonstrations and SIP revisions would
be due by April 2013.
D. What Are Attainment Dates for Any
New 2006 PM2.5 Standards?
Section 172(a)(2)(A) states that the
attainment date for a nonattainment area
must be ‘‘as expeditiously as
practicable, but no later than 5 years
from the date of designation for the
area.’’ If any new 2006 PM2.5
designations are made in December
2009 and have an effective date of April
2010, the initial attainment date for any
new PM2.5 standard would be no later
than April 2015. As an aside, this
attainment date would correspond with
the latest date an area designated in
April 2005 could come into attainment
with the 1997 PM2.5 NAAQS. For an
area with a maximum 5-year attainment
date, EPA would determine whether it
had attained the standard by evaluating
air quality data from the three previous
calendar years (2012–2014).
Section 172 also states that if EPA
deems it appropriate, the Agency may
extend the attainment date for an area
for a period not greater than 10 years
from the date of designation as
nonattainment, taking into account the
severity of the nonattainment problem
in the area, and the availability and
feasibility of pollution control measures.
For any area that is granted the full 5year attainment date extension, the
attainment date would be as
expeditiously as practicable, but no later
than April 2020. For such areas, EPA
would determine whether the area
attained the standard by evaluating air
quality data from 2017, 2018, and 2019.
Table 1 is an overview of the proposed
timeline for implementing any new
2006 PM2.5 standards.
TABLE 1.—PROPOSED TIMELINE FOR ANY NEW 2006 PM2.5 STANDARDS
Effective date of standard
December 2006
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Monitoring data used for State recommendations ...................................
State recommendations to EPA ...............................................................
Final designations signature .....................................................................
Effective date of designations ...................................................................
SIPs due ...................................................................................................
Attainment date .........................................................................................
Attainment date with a 5-year extension ..................................................
The EPA is soliciting comments on
which relevant factors should influence
EPA’s decision on any potential
timeline.
2005–2007.
December 2007.
December 2009.
April 2010.
April 2013.
Up to April 2015 (based on 2012–2014 data).
Up to April 2020 (based on 2017–2019 data).
V. What Are the Potential Timelines for
Implementation of Any New PM10–2.5
NAAQS?
A. What Is a Potential Schedule for Any
New PM10–2.5 Designation Process?
Section 107(d)(1)(B) gives the Agency
the authority to promulgate designations
for all areas as expeditiously as
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practicable, but no later than 3 years
from the date of promulgation of the
new or revised NAAQS.
Currently, a PM10–2.5 monitoring
network does not exist. The EPA’s
proposed monitoring regulations for
PM10–2.5 (71 FR 2710) call for monitors
to be deployed by January 2009. If this
schedule is adopted, the first period
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when 3 years of data would be available
for State designation recommendations
would be mid-2012 based on air quality
data for 2009–2011. As noted above,
following the statutory timeline,
designations for PM10–2.5 would be
required to occur no later than late
2009. Three years of PM10–2.5 monitoring
data will not be available at that time.
For EPA to meet its statutory obligation,
EPA would need to designate all areas
as unclassifiable under section
107(d)(1)(A)(iii), on the basis that no
information is available to determine
whether an area is meeting any new
NAAQS for PM10–2.5. From a historical
perspective this was the situation in
1997 when we established the PM2.5
NAAQS. Subsequent, to the
establishment of the PM2.5 NAAQS in
1997, Congress passed legislation which
modified the CAA for the purposes of
PM2.5 designations. EPA is potentially
confronting this issue again with respect
to any new PM10–2.5 NAAQS. As a
policy, EPA does not think that
designating all areas of the country as
unclassifiable provides useful
information to the public about their
area meeting new air quality standards.
EPA would prefer to not make
designations until three years of
monitoring data is available. EPA is
soliciting comments on the best way to
address this issue.
B. What Is EPA’s Preferred Schedule for
Designations for Any New PM10–2.5
Standards?
The first available 3 years of data from
a monitoring network for PM10–2.5 will
be 2009–2011. If EPA had not
previously designated areas
unclassifiable, EPA could then request
recommendations from States for areas
that might be designated nonattainment
for PM10–2.5 by July 2012. This is
approximately 6 months after a full 3
years of data would be available for
some areas. EPA believes this is
adequate time for evaluating and quality
assuring data to make recommendations
on designations. On the other hand,
States have until May 1 to certify that
their monitoring data is correct, and
may need additional time for
designation recommendations. Another
option would be to allow the States
until October 2012 to make
recommendations. The EPA would like
to take comment on this option.
Following submittal of designation
recommendations by the States, EPA
will evaluate the recommendations and
make modifications by December 2012.
States will be notified of these changes,
and given another opportunity to
comment on the proposed modifications
to designations. The EPA would then
issue final modified PM10–2.5
designations by May 2013 which would
be effective approximately July 2013.
If EPA had previously designated
areas unclassifiable, then, once EPA had
sufficient monitoring data available,
EPA would move forward in accordance
with the provisions of section
107(d)(3)(A) to notify States that it
believed designations for areas should
be revised. States would then have the
opportunity to respond in accordance
with section 107(d)(3)(B), and EPA
would take action regarding any
revisions of the designations in
accordance with section 107(d)(3)(C).
Since classifications under Title I are
done at the same time as designations,
EPA is considering the role a
classification system could play in
facilitating the implementation of any
new PM2.5 NAAQS. The EPA prefers not
to develop a classification system to use
in determining the amount of time
permitted for attainment, for reasons
similar to those outlined in the
Proposed Rule to Implement the Fine
Particle National Ambient Air Quality
Standards; Proposed Rule (70 FR page
66000, November 1, 2005). Developing a
classification system is only an option,
not a requirement under section
172(a)(1), and for the reasons noted EPA
does not believe it would be preferable
to implement a classification scheme.
The EPA would like comments on this
potential designation timeline, and on
its intentions to not develop a
classification system.
C. What Is EPA’s Preferred Schedule for
Attainment Demonstrations and SIP
Submittals for Any New PM10–2.5
Standards?
Section 172(b) of the CAA requires
EPA to establish a schedule for a State
to submit its attainment demonstration
and SIP revision within 3 years of
nonattainment designation. Following
the schedule outlined in part V(B)
above, if nonattainment designations for
any new PM10–2.5 standards were
effective in July 2013, then attainment
demonstrations and SIP revisions would
be due by July 2016. The EPA would
like comments on this proposed
timeline.
D. What Is EPA’s Preferred Schedule for
Attaining Any New PM10–2.5 Standards?
Section 172(a)(2)(A) states that the
attainment date for a nonattainment area
must be ‘‘as expeditiously as
practicable, but no later than 5 years
from the date of designation for the
area.’’ If new PM10–2.5 designations are
made in May 2013 and are effective in
July 2013, the initial attainment date for
PM10–2.5 would be as expeditiously as
practicable but no later than July 2018.
For an area with an attainment date of
July 2018, EPA would determine
whether it had attained the PM10–2.5
standards by evaluating air quality data
from the 3 previous calendar years (i.e.,
2015, 2016 and 2017).
Section 172 also states that if EPA
deems it appropriate, the Agency may
extend the attainment date for an area
for a period not greater than 10 years
from the date of designation, taking into
account the severity of the
nonattainment problem in the area, and
the availability and feasibility of
pollution control measures. For any area
that is granted the full 5-year attainment
date extension, the attainment date
would be no later than July 2023. For
such areas, EPA would determine
whether they have attained the standard
by evaluating air quality data from 2020,
2021 and 2022. Table 2 is an overview
of this proposed timeline for
designation, SIP submittal and
attainment dates under this proposed
schedule.
TABLE 2.—PROPOSED TIMELINE FOR A POSSIBLE 2006 PM10–2.5 STANDARDS
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Effective date of standard
December 2006
Monitoring data used for State recommendations ...................................
State recommendations to EPA ...............................................................
Final designations signature .....................................................................
Effective date of designations ...................................................................
SIPs due ...................................................................................................
Attainment date .........................................................................................
Attainment date with extension .................................................................
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2009–2011.
July 2012.
May 2013.
July 2013.
July 2016.
Up to July 2018 (based on 2015–2017 data).
Up to July 2023 (based on 2020–2022 data).
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The EPA requests comment on this
potential timeline for attaining any new
PM10–2.5 standards.
VI. How Should EPA Implement the
Transition From the PM10 Standards to
Any New PM10–2.5 Standards?
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A. What Is EPA’s Proposal for Revoking
the PM10 Standards?
Before areas are designated under any
new PM10–2.5 standards, we intend to
address how to transition from
implementation of the PM10 standards
to any new PM10–2.5 standards. As part
of the NAAQS proposal (71 FR 2620),
EPA proposed to revoke the annual
PM10 standard everywhere, and the 24hour PM10 standard everywhere except
in areas where there is at least one
monitor that is located in an urbanized
area with a minimum population of
100,000 people and that violates the 24hour PM10 standard based on the most
recent 3 years of data. This revocation
would be effective upon promulgation
of the PM NAAQS in December 2006.
The EPA also provided a list of places
where the 24-hour PM10 standard would
not be revoked under the proposal. In
addition, EPA requested comment on
whether the 24-hour PM10 standard
should be retained in areas that are
either urbanized areas with populations
less than 100,000 people or nonurbanized areas (i.e., population less
than 50,000) but where the majority of
the ambient mix of PM10–2.5 is generated
by high density traffic on paved roads,
industrial sources, and construction
sources, and which have at least one
monitor that violated the 24-hour PM10
standard. Comments on this revocation
plan should be submitted under that
notice (71 FR 2620).
This raises a number of issues for
those areas where the 24-hour PM10
standard would still apply including:
When and how should the 24-hour PM10
standard be revoked for these areas;
should anti-backsliding provisions
apply; how to address NSR and
maintenance issues; and other
implementation issues. Our principal
objective for the transition is to ensure
that air quality will not degrade in areas
where the potential new PM10–2.5
NAAQS would apply, and that areas
continue to make progress toward
attainment of the PM standards. Subject
to requirements under the CAA for
revising SIPs, EPA expects States would
take the opportunity to revise their SIPs
to reflect the revocation of the PM10
standards.
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B. What Should the Timing Be for
Revoking the 24-Hour PM10 Standard for
Those Areas Where the 24-Hour PM10
Standard Is Retained?
The EPA contemplates that the 24hour PM10 standard would be revoked
one year after attainment/nonattainment
designations are effective for a 24-hour
PM10–2.5 standard. Because attainment/
nonattainment designations would not
occur until July 2013, it is reasonable to
expect that some areas where the 24hour PM10 standard has not been
revoked would come into attainment
with the PM10 standard prior to July
2013. We invite comment on how these
areas should be treated.
C. What Transition Issues Are Created
by Revoking the 24-Hour PM10 Standard
in Areas Where It Is Currently Proposed
To Be Retained and How Might They Be
Addressed?
1. Control Measures
EPA wants to ensure that air quality
is not degraded if we move from one
version of the NAAQS to another. What
protections should remain in place to
ensure that air quality will not degrade
once the 24-hour PM10 standard is
revoked, and that progress will continue
as areas transition from implementing
the 24-hour PM10 standard to
implementing the 24-hour PM10–2.5
standard?
a. What requirements based on an
area’s classification for the PM10
standard should continue to apply?
The EPA believes an approach similar
to what was done under the ozone
transition from the 1-hour to the 8-hour
standard (69 FR 23951 page 23969)
would be appropriate here in that
control measures which remain in place
were determined by the area’s
classification. Such an approach would
mean that moderate PM10
nonattainment areas should continue to
require reasonably available control
measures (RACM) (as described in
section 189(a)(1)(C) of the CAA). Serious
PM10 nonattainment areas should also
continue to require best available
control measures (BACM) (section
189(b)(1)(B) of the CAA). All
nonattainment areas should have an
EPA-approved part D SIP in place, and
continue to implement the
nonattainment requirements and control
measures identified in the SIP. Any
effort to change SIP-approved measures
would be subject to a section 110(l)
demonstration of no interference with
applicable requirements.
The EPA also believes that those areas
where the 24-hour PM10 standard is
being violated and has not been revoked
should continue to implement the
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6725
requirements of the CAA until
nonattainment and attainment
designations for PM10–2.5 are completed.
However, this could represent a
significant period of time (from 2006–
2013). Consequently, EPA is interested
in alternative views regarding the
appropriate implementation pathway
for the PM10 standard in these areas.
b. How should EPA address
maintenance? Those PM10
nonattainment areas where the 24-hour
PM10 standard has not been revoked
which come into attainment with the
24-hour PM10 NAAQS prior to
designations under the 24-hour PM10–2.5
standard, may request to be
redesignated as attainment for PM10
under section 107(d). As such they
would need to submit a maintenance
plan under section 175A. Maintenance
areas do not have any outstanding
obligation to adopt further mandatory
control obligations. We would
anticipate an approach to maintenance
requirements similar to what was
provided in the ozone rule where
maintenance areas retain the discretion
to modify any discretionary control
measures upon a demonstration under
section 110(l) (69 FR 23951 page 23955).
The EPA requests comments on how to
address maintenance areas.
2. Transportation Conformity
Transportation conformity is required
under section 176(c) of the CAA (42
U.S.C. 7506(c)) to ensure that federally
supported highway and transit project
activities are consistent with (conform
to) the purpose of a SIP. Conformity to
the purpose of a SIP means that
transportation activities will not cause
new air quality violations, worsen
existing violations, or delay timely
attainment of the NAAQS.
Transportation conformity applies in
nonattainment areas and maintenance
areas. The EPA’s transportation
conformity rule, 40 CFR part 93,
establishes the criteria and procedures
for determining whether transportation
activities conform to the State air
quality plan. It also establishes criteria
and procedures for determining whether
transportation activities conform in
areas where no SIP containing motor
vehicle emissions budgets yet exists.
Transportation conformity
rulemakings, as well as other relevant
conformity materials such as guidance
documents, policy memoranda, the
complete text of the conformity rule,
and conformity research can be found at
EPA’s transportation conformity Web
site, at https://www.epa.gov/otaq/
transp.htm (once at the site, click on
‘‘Transportation Conformity.’’
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Until areas are designated
nonattainment, transportation
conformity will not apply for any new
PM10–2.5 standard. Based on the timeline
outlined above, designations for any
new PM10–2.5 NAAQS could be effective
in July 2013, and for all nonattainment
areas transportation conformity would
then apply 1 year later. Prior to the
designation date, EPA would propose to
update the transportation conformity
rule to address any new PM10–2.5
standard.
The EPA will solicit public comment
on these and other issues associated
with determining transportation
conformity in any new PM10–2.5
nonattainment areas when it proposes to
revise the conformity rule to address the
new standard. Once we revoke the PM10
standard and the associated
designations, transportation conformity
will no longer apply under the terms of
the statute for that standard.
3. General Conformity
Section 176(c) of the CAA requires
that before a Federal entity takes an
action, it must make a determination
that the proposed action will not
interfere with the SIP or the State’s
ability to attain and maintain the
NAAQS. In November 1993, EPA
promulgated two sets of regulations to
implement section 176(c). One set,
known as the general conformity
regulations, deals with all other Federal
activities besides funding of highway
and mass transit projects. These
activities include funding and approval
of airport projects, expansion of military
bases, and permitting of projects to
deepen waterways.
Federal agencies take thousands of
actions every day and requiring
determinations on every action would
not be possible. Therefore, EPA
established a number of exemptions to
the rule requirements including a de
minimis emission level generally based
upon the size of a major stationary
source in the nonattainment or
maintenance area.
Following are a series of questions
related to implementation of general
conformity on which EPA is soliciting
input:
• What de minimis levels should EPA
establish for direct and precursor
emissions for any new PM10–2.5
standards? The EPA currently does not
have speciated monitoring data for
PM10–2.5. Consequently, we do not know
if the mass of PM10–2.5 contains a
significant amount of particulate matter
formed by atmospheric chemical
reactions.
• In transitioning to a new standard,
how should EPA treat previous
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conformity evaluations and
determinations based on the PM10
standard?
• Are there any categories of actions
that should be exempt from the
conformity requirements for any new
PM10–2.5 standards? If so, how could
such exemptions be devised?
4. New Source Review Program
The NSR program is a preconstruction
permitting program that applies when a
new source is constructed or an existing
one is modified. The major NSR
program applies to major stationary
sources and is comprised of the
Prevention of Significant Deterioration
(PSD) program that applies in
attainment areas and a nonattainment
NSR program that applies to pollutants
for which an area is designated
nonattainment.
There are many major NSR program
implementation issues that EPA will
address for a new PM10–2.5 NAAQS,
including revocation of the existing
PM10 NAAQS. In this ANPR, EPA is
highlighting some of the key issues and
providing EPA’s preliminary thinking
on approaches for addressing them. We
recognize that there may be other
implementation issues not identified
here, and we invite you to identify
them. When submitting comments,
please support your comments with
adequate data and/or practical scenarios
or illustrations.
a. Does PM10 continue to be a
regulated NSR pollutant for PSD in
areas where the 24-hour PM10 NAAQS
would be revoked?
The PSD program applies when a
major stationary source of any
‘‘regulated NSR pollutant’’, that is
located in an area designated as
attainment or unclassifiable for any
criteria pollutant, is constructed or
undergoes a major modification (40 CFR
52.21(a)(2); 40 CFR 51.166(a)(7)). EPA
defines a ‘‘regulated NSR pollutant’’ to
include (1) any pollutant for which a
NAAQS has been promulgated
(otherwise known as a ‘‘criteria’’
pollutant); (2) any pollutant subject to a
NewSource Performance Standard
promulgated under section 111 of the
CAA; and (3) any pollutant that is
otherwise regulated under the Act,
except for hazardous air pollutants
regulated under section 112 of the Act 3
(40 CFR 52.21(b)(50); 40 CFR
51.166(b)(49)). Thus, in addition to
applying to criteria pollutants for which
EPA has promulgated a NAAQS, the
3 This definition also covers any pollutant that is
subject to any standard promulgated under or
established by Title VI of the Act, but this is not
relevant to particulate matter.
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PSD program also applies to any noncriteria pollutant that is covered by the
additional prongs of the definition of a
‘‘regulated NSR pollutant’’ described
above. However, not all of the PSD
program requirements outlined below
are applicable to non-criteria pollutants
that are subject to the PSD program.
The PSD requirements include but are
not limited to:
• Installation of Best Available
Control Technology (BACT),
• Air quality monitoring and
modeling analyses to ensure that a
project’s emissions will not cause or
contribute to a violation of any NAAQS
or maximum allowable pollutant
increase (PSD increment),
• Notification of Federal Land
Manager when a proposed source or
modification may affect nearby Class I
areas, and
• Public comment on the permit.
For any criteria pollutant subject to
PSD, all PSD requirements including the
PSD increments analyses apply.
However, since there are no NAAQS for
non-criteria pollutants, only some
requirements, including BACT, apply to
these pollutants (See 42 U.S.C.
7475(a)(4); 40 CFR 52.21(j)); 40 CFR
52.166(j)).
The proposed revocation of the 24hour PM10 NAAQS in certain areas
raises issues about whether existing PSD
regulations would continue to apply to
PM10 in any respect after the revocation
of the NAAQS in these areas. The extent
to which all or some of the PSD
requirements apply depends on whether
PM10 continues to be a regulated NSR
pollutant in these areas, either as a
criteria or a non-criteria pollutant,
under EPA’s regulations and the CAA.
We seek comment on the following
options to address these issues:
Option 1. Since the 24-hour PM10
standard would remain in effect at least
in some areas, we could conclude that
PM10 continues to be a regulated NSR
pollutant for the PSD program. Thus,
even in those areas in which the 24hour PM10 NAAQS is revoked (24-hour
revoked areas), PM10 would be regarded
as a regulated NSR pollutant only by
virtue of being otherwise subject to
regulation under the CAA (40 CFR
52.21(b)(50)(iv)) because a 24-hour PM10
NAAQS continues to apply in other
areas. Under this approach, PSD for
PM10 would continue to apply in all
areas. However, as stated earlier, only a
few PSD requirements, including BACT,
would apply in 24-hour revoked areas
since PM10 would be regarded as a noncriteria pollutant in those areas. In those
areas where the 24-hour PM10 NAAQS
is not revoked, all PSD program
elements would continue to apply for
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PM10 because it remains a criteria
pollutant in these areas.
Option 2. Alternatively, we could
interpret all prongs of the ‘‘regulated
NSR pollutant’’ definition to be areaspecific. Thus, in 24-hour revoked areas,
PM10 would no longer be a criteria
pollutant, and none of the other prongs
of the definition of ‘‘regulated NSR
pollutant’’ would apply to PM10 in these
areas. Therefore, none of the PSD
requirements would apply to PM10 in
such areas. We request comment on
whether there is any other basis for
retaining PM10 as a regulated NSR
pollutant, even if it is no longer a
criteria pollutant.
b. Does the CAA require continued
obligation for some form of PM
increment?
Section 163 of the CAA states that
each SIP should contain measures
assuring that maximum allowable
increases over baseline concentration
(increments) for PM shall not be
exceeded in attainment areas. Section
163 contains specific numerical
increments (expressed as µg/m3) for PM,
which EPA initially implemented using
the total suspended particulate
indicator. After EPA transitioned to
PM10 as the indicator for PM in 1987,
the Agency substituted PM10 increments
for the PM increments in section 163
based on the authority of section 166(f)
of the Act (58 FR 31622, June 3, 1993).
Section 166(f), which was enacted in the
1990 amendments to the CAA,
authorized EPA to substitute PM10
increments ‘‘of equal stringency in
effect’’ as the section 163 PM
increments, but also required that the
PM increments remain in effect until the
new PM10 increments were
promulgated.
For pollutants other than PM and
sulfur dioxide,4 Section 166(a) of the
CAA directs the Administrator to
conduct a study and promulgate
regulations, which may include
increments, to prevent significant
deterioration of air quality. EPA
promulgated increments for nitrogen
oxides under this authority (70 FR
59582, Oct. 12, 2005, and 53 FR 40656,
Oct. 17, 1988). Section 166(a) also
directs the Administrator to promulgate
pollutant-specific PSD regulations for
pollutants for which NAAQS are
promulgated after 1977. The proposed
revocation of the PM10 NAAQS raises
two issues with respect to EPA’s PSD
regulations for PM. The first is whether
EPA has a continuing obligation under
section 163 or 166(f) of the CAA to
implement some form of a PM
4 Section 163 also contains increments for sulfur
dioxide. 42 U.S.C. 7473.
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increment. The second question
concerns the methodology that EPA
should use to establish PSD regulations
for PM2.5 and PM10–2.5 to replace the
increments for PM10. We seek comment
on the following options to address
these issues:
Option 1. Once the PM10 NAAQS is
revoked, one approach would be to
conclude that section 166(f), requiring
equivalent PM10 increments, is no
longer applicable in the absence of a
PM10 NAAQS. Furthermore, since
section 166(f) effectively superseded
section 163, we would not construe the
latter provision to require that EPA
maintain a PM increment after the
revocation of the PM10 NAAQS. Thus,
we could conclude that neither the
section 163 increment requirement for
PM nor the section 166(f) increment
requirement for PM10 remains effective
after revocation of the PM10 standard.
Accordingly, we would need to
develop new increments 5 for PM2.5 and
PM10–2.5. In the interest of simplicity
and ease of implementation, we could
develop new increments for PM2.5 and
PM10–2.5 pursuant to section 166 of the
CAA. This approach would include
among other things, establishing new
baseline dates and trigger dates for PM2.5
and PM10–2.5 on the theory that these are
separate, new pollutants, at least for
NSR purposes. Otherwise the alternative
approach, described below, of trying to
continue the implementation of the
section 163 increments for PM (using
the new indicators) would involve
retroactively estimating PM2.5 and
PM10–2.5 emissions in 1978 (based on the
original PSD requirements for PM), and
would be extremely difficult in most
cases.
Option 2. Another approach would be
to interpret sections 163 and 166(f) to
require some form of PM increments on
a continuous basis. However, we would
recognize the Congressional intent
reflected in section 166(f) that EPA
update the PM increments as it modifies
the NAAQS for PM. Under this option,
we could substitute PM10 increments
with two new increments (PM2.5 and
PM10–2.5) ‘‘of equal stringency in effect’’
based on section 166(f) of the CAA by
using the methodology reflected in our
1993 PM10 increments regulation. This
approach would provide continuity
with the existing PM10 increments
system and would most likely involve
retaining the existing baseline areas and
dates.
5 Alternatively, if we promulgate such regulations
under section 166, EPA could develop equivalent
PSD regulations for PM2.5 and PM10–2.5 that include
other measures instead of increments.
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c. How should permitting authorities
implement the PM2.5 program upon
revocation of the PM10 NAAQS?
When EPA first promulgated the
NAAQS for PM2.5 in 1997, we
encountered a number of technical
difficulties with implementing the PSD
program for PM2.5 upon the effective
date of the NAAQS for PM2.5. To
address these difficulties, EPA
established a policy that enabled
permitting authorities to use the
implementation of the PSD program for
PM10 as a surrogate for a PM2.5 PSD
program until the necessary tools were
in place to measure PM2.5 and
implement PSD permitting programs for
PM2.5. See Memorandum from John S.
Seitz, Director, Office of Air Quality
Planning and Standards, to Regional Air
Directors, Interim Implementation of
New Source Review for PM2.5 (October
23, 1997) at: https://www.epa.gov/
Region7/programs/artd/air/nsr/
nsrmemos/pm25.pdf. The EPA extended
this PM10 surrogate policy to
implementation of the NSR program in
nonattainment areas, once PM2.5
nonattainment designations became
effective on April 5, 2005. See
Memorandum from Stephen D. Page,
Director, Office of Air Quality Planning
and Standards, to Regional Air
Directors, Interim Implementation of
New Source Review for PM2.5 in
Nonattainment Areas (April 5, 2005) at:
https://www.epa.gov/Region7/programs/
artd/air/nsr/nsrmemos/pm25guid.pdf).
These policies remain in effect today
pending the promulgation of EPA’s
PM2.5 implementation rules for NSR and
approval of SIPs containing PSD
programs for PM2.5.
Because of the proposed revocation of
the PM10 NAAQS, there may not be a
PM10 PSD program remaining in 24hour revoked areas to rely upon as a
surrogate for implementation of a PSD
program for PM2.5. This raises the issue
of how States may continue to satisfy
the PSD program requirements for PM2.5
in the interim period. We seek comment
on the following options to address this
issue:
Option 1. One approach that we might
use would be to continue using an
analysis of PM10 air quality as a
surrogate for the air quality analysis
under the PM2.5 program with a change.
Permitting authorities may continue to
analyze PM10 emissions and
concentrations, but they would have to
compare these concentrations with the
PM2.5 NAAQS to show that the
predicted PM10 concentrations would
not exceed the PM2.5 NAAQS. This
approach would overpredict actual
PM2.5 concentrations in most cases, but
it would represent a conservative
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screening mechanism that could
demonstrate that a new source or major
modification would not cause or
contribute to a violation of the PM2.5
NAAQS. We believe that this would be
a suitable interim approach until all the
necessary implementation elements for
carrying out an independent PM2.5
program have been finalized.
Option 2. An alternative approach
would be to continue to apply the
existing surrogate policy for
implementing the PM2.5 program, even
after the PM10 standard has been
revoked. In other words, the impacts of
the PM10 emissions would continue to
be compared with the former PM10
NAAQS. Again this would serve as an
interim policy, until all the PM2.5
implementation elements for carrying
out an independent PM2.5 program have
been finalized.
d. How should EPA implement the
PSD program for PM10–2.5 upon the
effective date of the promulgation of the
PM10–2.5 NAAQS?
The EPA has interpreted various
provisions in title I, part C of the CAA
to require immediate implementation of
the PSD program in all areas for each
pollutant upon the effective date of a
NAAQS for that pollutant. See
SeitzMemorandum (October 27, 1997).
As noted earlier, EPA’s PSD regulations
define a regulated NSR pollutant to
include, among other things, any
pollutant for which a NAAQS is
promulgated (40 CFR 51.166(b)(49);
52.21(b)(50)). In contrast, under part D
of the CAA, the nonattainment NSR
program is not required to be
implemented for a particular pollutant
subject to a NAAQS until nonattainment
areas are designated pursuant to section
107 of the CAA, and are in effect for that
pollutant.
As described in detail in the earlier
PM2.5 implementation discussion, EPA
established a policy that enabled
permitting authorities to use the
implementation of a PSD program for
PM10 as a surrogate for implementation
of the PSD program for PM2.5 until the
necessary tools were in place to measure
PM2.5 and implement permitting
programs for PM2.5. The EPA anticipates
that it will encounter similar difficulties
with implementing a PSD program for
PM10–2.5 upon the effective date of a
NAAQS for PM10–2.5. However, as
discussed above in the context of PM2.5,
the revocation of the PM10 NAAQS may
leave EPA without a PM10 program to
rely upon as a surrogate for
implementation of a PSD program for
PM10–2.5. Thus, we are exploring other
approaches that EPA might use to fulfill
the PSD requirements in title I, part C
of the CAA upon the effective date of a
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NAAQS for PM10–2.5. We request
comment on the following approaches
and welcome suggestions for additional
approaches we might use for a
temporary, interim period to prevent
significant deterioration of air quality
from new and modified sources of
PM10–2.5:
Option 1. One approach that we might
use would be to continue using an
analysis of PM10 air quality as a
surrogate for the air quality analysis
under a PM10–2.5 program. Permitting
authorities may continue to analyze
PM10 emissions and concentrations and
compare that with the PM10–2.5 NAAQS
to show that the predicted PM10
concentrations would not exceed the
PM10–2.5 NAAQS. This approach would
overpredict actual PM10–2.5
concentrations in most cases, but it
would represent a conservative
screening mechanism that could
demonstrate that a new source or major
modification would not cause or
contribute to a violation of the PM10–2.5
NAAQS.
Option 2. Another approach might be
to compare the PM10 analysis to the
former PM10 NAAQS and thus use
compliance with the former PM10
NAAQS as a surrogate for compliance
with the new PM10–2.5 NAAQS for a
temporary period. This latter approach
might be used independently or as a
secondary step in a tiered analysis if the
first approach discussed above was
found to be overly conservative.
Option 3. Another approach might be
to use compliance with BACT for
PM10–2.5 as a surrogate for the PM10–2.5
NAAQS compliance demonstration. In
this approach, we might make a
determination for an interim period that
the first major sources that trigger PSD
requirements for PM10–2.5 are not likely
to cause or contribute to noncompliance
with the PM10–2.5 NAAQS if they meet
BACT for PM10–2.5. Thus, we might
consider compliance with BACT to
represent a surrogate for the PM10–2.5
NAAQS compliance demonstration for a
limited period until we have the tools
in place to assess PM10–2.5
concentrations.
e. How should ambient PM10–2.5
dominated by rural windblown dust and
soils, and generated by agricultural and
mining sources be treated in the NSR
program for the proposed PM10–2.5
standard?
The proposed PM10–2.5 indicator is
qualified so as to include any ambient
mix of PM10–2.5 that is dominated by
resuspended dust from high density
traffic on paved roads and PM generated
by industrial sources and construction
sources, and excludes any ambient mix
of PM10–2.5 that is dominated by rural
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windblown dust and soils and PM
generated by agricultural and mining
sources. This suggests that the NSR
applicability test would exclude these
sources from consideration. We request
comment on how we would implement
the NSR program if we promulgate a
NAAQS with these characteristics.
VII. What Emission Inventory
Requirements Should Apply Under Any
New PM 2.5 and PM10–2.5 NAAQS?
Emission inventories are critical for
the efforts of State, local, tribal and
Federal agencies to attain and maintain
the NAAQS that EPA has established for
criteria pollutants including PM2.5 and
any new PM10–2.5 standards. Pursuant to
its authority under section 110 of Title
I of the CAA, EPA has long required
States to submit emission inventories
containing information regarding the
emissions of criteria pollutants and their
precursors. The EPA codified these
requirements in 40 CFR part 51, subpart
Q in 1979 and amended them in 1987.
In June 2002, EPA promulgated the
Consolidated Emissions Reporting Rule
(CERR)(67 FR 39602, June 10, 2002).
The CERR consolidates the various
emissions reporting requirements into
one place in the CFR. In January 2006,
EPA proposed the Air Emissions
Reporting Requirements (AERR) (71 FR
69, January 3, 2006) which proposes to
modify some of the reporting
requirements established by CERR. In
addition, EPA has developed guidance
‘‘Emissions Inventory Guidance for
Implementation of Ozone and
Particulate Matter National Ambient Air
Quality Standards (NAAQS) and
Regional Haze Regulations, EPA–454/R–
99–006 available at: https://
www.epa.gov/ttn/chief/eidocs/eiguid/
index.html. The EPA developed this
guidance document to complement the
CERR and proposed AERR and to
provide specific guidance to State and
local agencies and Tribes on how to
develop emissions inventories for 8hour ozone, PM2.5, and regional haze
SIPs. The CERR and AERR set forth
national requirements for emission data
elements for all States, regardless of
NAAQS attainment status. EPA
guidance complements these
requirements and indicates how the
data should be prepared for SIP
submissions. The SIP inventory, which
may be derived from the CERR
inventory, applies only to
nonattainment areas. The SIP inventory
also must be approved by EPA as a SIP
element and is therefore subject to
public hearing requirements, and is thus
regulatory in nature. The inventory
required by the CERR is not. Because of
the regulatory significance of the SIP
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inventory, EPA will need more
documentation on how the SIP
inventory was developed by the State as
opposed to the documentation required
for the CERR inventory.
Therefore, the basis for EPA’s
emission inventory program is specified
in the CERR, the AERR notice of
proposed rulemaking (NPRM) and the
related guidance document. The EPA is
interested in receiving comments on
whether or not additional emission
inventory requirements or guidance are
needed to implement any new PM2.5
standards and any new PM10–2.5
NAAQS. Following are a set of
questions on which we would like
input:
a. Are the data elements specified
within the CERR and AERR sufficient to
develop adequate SIPs for PM2.5 and
PM10–2.5? For example, should EPA
expand the listing of reportable
compounds to include elemental and
organic carbon?
b. Fugitive emissions are a significant
contributor to ambient levels of PM10–2.5.
Should EPA require and/or develop
more precise methods for estimating
fugitive particulate emissions, perhaps
including wind blown dust?
c. The EPA believes that daily
emissions will be important under both
PM2.5 and PM10–2.5. Should EPA require
any additional emission inventory data
elements or temporal allocation
techniques to estimate more accurately
daily emissions and their variability?
d. Are there other inventory issues
that EPA should define through either
regulation or guidance?
VIII. Statutory and Executive Order
Reviews
Under Executive Order 12866,
Regulatory Planning and Review (58 FR
51735, October 4, 1993), this action is
not a ‘‘significant regulatory action’’ and
is, therefore, not subject to review by the
Office of Management and Budget.
List of Subjects in 40 CFR Part 51
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Environmental protection, Particulate
matter.
Dated: February 3, 2006.
Stephen L. Johnson,
Administrator.
[FR Doc. E6–1798 Filed 2–8–06; 8:45 am]
BILLING CODE 6560–50–P
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 51
[OAR–2005–0124; FRL–8030–1]
RIN 2060–AN34
Air Quality: Revision to Definition of
Volatile Organic Compounds—
Exclusion of HFE–7300
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: This action proposes to revise
EPA’s definition of volatile organic
compounds (VOC) for purposes of
preparing State implementation plans
(SIPs) to attain the national ambient air
quality standards (NAAQS) for ozone
under title I of the Clean Air Act (CAA).
This proposed revision would add
1,1,1,2,2,3,4,5,5,5-decafluoro-3methoxy-4-trifluoromethyl-pentane
[also known as HFE–7300 or L–14787 or
C2F5CF(OCH3)CF(CF3)2] to the list of
compounds excluded from the
definition of VOC on the basis that this
compound makes a negligible
contribution to tropospheric ozone
formation. If you use or produce HFE–
7300 and are subject to EPA regulations
limiting the use of VOC in your product,
limiting the VOC emissions from your
facility, or otherwise controlling your
use of VOC for purposes related to
attaining the ozone NAAQS, then you
will not count HFE–7300 as a VOC in
determining whether you meet these
regulatory obligations. This action may
also affect whether HFE–7300 is
considered as a VOC for State regulatory
purposes, depending on whether the
State relies on EPA’s definition of VOC.
As a result, if you are subject to certain
Federal regulations limiting emissions
of VOCs, your emissions of HFE–7300
may not be regulated for some purposes.
DATES: Comments on this proposal must
be received by March 13, 2006. Requests
for a hearing must be submitted by
February 24, 2006.
ADDRESSES: Submit your comments,
identified by Docket ID No. OAR–2005–
0124, by one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Agency Web site: https://
www.epa.gov/edocket. EDOCKET, EPA’s
electronic public docket and comment
system, is EPA’s preferred method for
receiving comments. Follow the on-line
instructions for submitting comments.
• E-mail: Send e-mail to the EPA
Docket Center at a-and-rDocket@epa.gov.
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• Fax: Send faxes to the EPA Docket
Center at (202) 566–1741.
• Mail: Environmental Protection
Agency, Mailcode: 6102T, 1200
Pennsylvania Ave., NW., Washington,
DC 20460. Attn: Docket No. OAR–2005–
0124, ‘‘Air Quality: Revision to
Definition of Volatile Organic
Compounds—Exclusion of HFE–7300.’’
Please include a total of two copies.
• Hand Delivery: EPA Docket Center,
U.S. Environmental Protection Agency,
EPA West Building, Room B102, 1301
Constitution Avenue, NW., Washington,
DC. Such deliveries are only accepted
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. OAR–2005–0124. 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.epa.gov/
edocket, 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 EDOCKET,
regulations.gov, or e-mail. The EPA
EDOCKET and the Federal
regulations.gov Web sites are
‘‘anonymous access’’ systems, 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
EDOCKET or regulations.gov, your email 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, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses.
Docket: All documents in the docket
are listed in the EDOCKET index at
https://www.epa.gov/edocket. Although
listed in the index, some information is
not publicly available, i.e., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
E:\FR\FM\09FEP1.SGM
09FEP1
Agencies
[Federal Register Volume 71, Number 27 (Thursday, February 9, 2006)]
[Proposed Rules]
[Pages 6718-6729]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E6-1798]
=======================================================================
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 51
[EPA-HQ-OAR-2005-0175; FRL-8030-6]
Transition to New or Revised Particulate Matter (PM); National
Ambient Air Quality Standards (NAAQS)
AGENCY: Environmental Protection Agency (EPA).
ACTION: Advance Notice of Proposed Rulemaking (ANPR).
-----------------------------------------------------------------------
SUMMARY: The EPA recently issued a notice of proposed revisions to the
national ambient air quality standards (NAAQS) for particulate matter
(PM). EPA will take final action on the proposal by September 27, 2006.
This notice provides advance notice of key issues for consideration in
the development of potentially new or revised policies and/or
regulations to implement revisions to the NAAQS for PM recognizing that
no final decision has been made concerning whether or how to revise the
PM NAAQS. The EPA is posing a number of questions related to the
transition from the current to potentially revised PM2.5
standards, as well as the transition from the current PM10
standards to potentially new PM10-2.5 standards. In this
ANPR, EPA is soliciting comment on the Agency's preferred approaches to
revocation of the 1997 PM2.5 standards once any new 2006
PM2.5 standards would be in place, and also approaches to
revocation of the 24-hour PM10 standard in areas where it
would remain after promulgation of any new PM10-2.5
standards. The EPA is also highlighting and providing preliminary
thinking on how to address some of the key New Source Review (NSR)
issues related to the new PM10-2.5 standards, and the
transition from PM10 standards to PM10-2.5
standards. Finally, EPA is requesting comment on potential timeframes
for designations, attainment demonstrations and State Implementation
Plan (SIP) submittals and attainment dates for both any new
PM2.5 and PM10-2.5 standards.
DATES: Comments must be received on or before April 10, 2006.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2005-0175, 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, Attention Docket ID No.
EPA-HQ-OAR-2005-0175.
Fax: Fax your comments to (202) 566-1741, Attention Docket
ID. No. EPA-HQ-OAR-2005-0175.
Mail: Docket EPA-HQ-OAR-2005-0175 Environmental Protection
Agency, Mail Code: 6102T, 1200 Pennsylvania Ave., NW., Washington, DC,
20460. Please include a total of two copies.
Hand Delivery: Deliver your comments to: Air Docket,
Environmental Protection Agency, 1301 Constitution Avenue, NW., Room
B102, Washington, DC 20004, Attention Docket ID No. EPA-HQ-OAR-2005-
0175. Such deliveries are only accepted during the Docket's normal
hours of operation, and special arrangements should be made for
deliveries of boxed information.
[[Page 6719]]
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2005-0175. The 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 https://
www.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, EPA recommends that you include your name
and other contact information in the body of your comment 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 further information about EPA's public docket visit the
EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
For additional instruction on submitting a comment, go to ``What Should
I Consider as I Prepare My Comments for the EPA?'' of the SUPPLEMENTARY
INFORMATION section of this document.
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 EPA Docket Center,
EPA/DC, EPA West, Room B102, 1301 Constitution Avenue, 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. A reasonable fee may be
charged for copying. The telephone number for the Public Reading Room
is (202) 566-1744, and the telephone number for the Air Docket is (202)
566-1742.
FOR FURTHER INFORMATION CONTACT: For questions regarding PM
implementation issues, contact Ms. Barbara Driscoll, U.S. Environmental
Protection Agency, Office of Air Quality Planning and Standards, Mail
Code C504-02, Research Triangle Park, NC 27711, phone number (919) 541-
1051 or by e-mail at: driscoll.barbara@epa.gov. Regarding NSR issues,
contact Raj Rao, U.S. Environmental Protection Agency, Office of Air
Quality Planning and Standards, Mail Code C339-03, Research Triangle
Park, NC 27711, phone number (919) 541-5344 or by e-mail at
rao.raj@epa.gov.
SUPPLEMENTARY INFORMATION:
How Should I Submit CBI to the Agency?
Do not submit information that you consider to be CBI through
https://www.regulations.gov or e-mail. Clearly mark the part or all of
the information that you claim to be CBI.
For CBI information in a disk or CD-ROM that you mail to EPA, mark
the outside of the disk or CD-ROM as CBI and then identify
electronically within the disk or CD-ROM the specific information that
is claimed as CBI. In addition to one complete version of the comment
that includes information claimed as CBI, a copy of the comment that
does not contain the information claimed as CBI must be submitted for
inclusion in the public docket. Information so marked will not be
disclosed except in accordance with procedures set forth in 40 CFR part
2. Send or deliver information identified as CBI only to the following
address: Roberto Morales, U.S. EPA, Office of Air Quality Planning and
Standards, Mail Code C404-02, Research Triangle Park, NC 27711,
telephone (919) 541-0880, e-mail at morales.roberto@epa.gov, Attention
Docket ID No. EPA-HQ-OAR-2005-0175.
What Should I Consider as I Prepare My Comments for EPA?
You may find the following suggestions helpful for preparing your
comments:
1. Explain your views as clearly as possible.
2. Describe any assumptions that you used.
3. Provide any technical information and/or data you used that
support your views.
4. If you estimate potential burden or costs, explain how you
arrived at your estimate.
5. Provide specific examples to illustrate your concerns.
6. Offer alternatives.
7. Make sure to submit your comments by the comment period deadline
identified.
8. To ensure proper receipt by EPA, identify the appropriate docket
identification number in the subject line on the first page of your
response. It would also be helpful if you provided the name, date, and
Federal Register citation related to your comments.
Table of Contents
I. What Actions Related to the PM NAAQS Have Recently Been Proposed
or Will Soon Be Proposed Which Relate to This Notice?
A. National Ambient Air Quality Standards for Particulate Matter
B. Revisions to Ambient Air Monitoring Regulations
C. Treatment of Data Influenced by Exceptional Events
II. What Is EPA'S Strategy for Addressing PM?
A. The State Implementation Plan (SIP) System
B. National Rules
III. How Should EPA Implement the Transition From the 1997
PM2.5 NAAQS to Any New 2006 PM2.5 NAAQS?
A. What Is the Status of Areas Designated Under the 1997
PM2.5 NAAQS?
B. How Might EPA Implement the Transition from the 1997
PM2.5 NAAQS to Any New 2006 PM2.5 NAAQS?
1. PM2.5 NAAQS Option 1
2. PM2.5 NAAQS Option 2
IV. What Are the Potential Timelines for Implementation of Any New
2006 PM2.5 NAAQS?
A. How Would the Implementation Schedules of the 1997
PM2.5 NAAQS and Any New 2006 PM2.5 NAAQS Fit
Together if the Revised PM2.5 Standards Are More
Stringent Than the Current Standards?
B. What Is EPA's Preferred Schedule for Any New 2006
PM2.5 Designation Process?
C. What Would the Schedule Be for Attainment Demonstrations and
SIP Submittals for Any New 2006 PM2.5 Standards?
D. What Are Attainment Dates for Any New 2006 PM2.5
Standards?
V. What Are the Potential Timelines for Implementation of Any New
PM10-2.5 NAAQS?
A. What Is a Potential Schedule for Any New PM10-2.5
Designation Process?
B. What Is EPA's Preferred Schedule for Designations for any New
PM10-2.5 Standards?
C. What Is EPA's Preferred Schedule for Attainment
Demonstrations and SIP Submittals for Any New PM10-2.5
Standards?
D. What Is EPA's Preferred Schedule for Attaining Any New
PM10-2.5 Standards?
[[Page 6720]]
VI. How Should EPA Implement the Transition From the PM10
Standards to Any New PM10-2.5 Standards?
A. What Is EPA's Proposal for Revoking the PM10
Standards?
B. What Should the Timing Be for Revoking the 24-Hour
PM10 Standard for Those Areas Where the 24-Hour
PM10 Standard Is Retained?
C. What Transition Issues Are Created by Revoking the 24-Hour
PM10 Standard in Areas Where It is Currently Proposed to
be Retained and How Might They be Addressed?
1. Control Measures
2. Transportation Conformity
3. General Conformity
4. New Source Review Program
VII. What Emissions Inventory Requirements Should Apply Under Any
New PM2.5 and PM10-2.5 NAAQS?
VIII. Statutory and Executive Order Reviews
I. What Actions Related to the PM NAAQS Have Recently Been Proposed or
Will Soon Be Proposed Which Relate to This Notice?
This ANPR is intended to solicit input into key issues related to
the transition to any new or revised NAAQS for PM. The EPA has proposed
two rulemakings, the NAAQS for Particulate Matter; Proposed Rule (71 FR
2620, January 17, 2006) and the Revisions to Ambient Air Monitoring
Regulations (71 FR 2710, January 17, 2006), and will be proposing
another rulemaking, Treatment of Data Influenced by Exceptional Events
(anticipated to be published by March 2006). These proposals are
summarized here to provide background for the issues and questions
raised in this document. The EPA is not taking comment on these actions
here. Rather, if you have comments, you should submit them to the
docket for the proposed rulemaking to which they are applicable,
following the procedures described in each proposal.
A. National Ambient Air Quality Standards for Particulate Matter
On December 20, 2005, the Administrator signed a notice proposing
revisions to the primary and secondary NAAQS for PM, which was
published on January 17, 2006 (71 FR 2620). The proposal can be found
at: https://www.epa.gov/oar/particlepollution/actions.html. For the
primary standards for fine particles (particles generally less than or
equal to 2.5 micrometers ([mu]m) in diameter, or PM2.5), EPA
proposed to revise the level of the 24-hour PM2.5 standard
from 65 micrograms per cubic meter ([mu]mg/m3) to 35 [mu]g/
m3, providing increased protection against health effects
associated with short-term exposure (including premature mortality and
increased hospital admissions and emergency room visits) and to retain
the level of the annual PM2.5 standard at 15 [mu]g/
m3, continuing protection against health effects associated
with long-term exposure (including premature mortality and development
of chronic respiratory disease). The EPA is also taking comment on
alternative NAAQS levels. Additionally, EPA proposed to revise the
criteria for spatial averaging of monitors for purposes of the annual
PM2.5 standard.
In addition, for the primary standards for coarse particles
generally less than or equal to 10[mu]m in diameter (PM10),
EPA proposed to revise the 24-hour PM10 standard in part by
establishing a new indicator for thoracic coarse particles (particles
generally between 2.5 and 10[mu]m in diameter, PM10-2.5),
qualified so as to include any ambient mix of PM10-2.5 that
is dominated by resuspended dust from high-density traffic on paved
roads and PM generated by industrial sources and construction sources,
and exclude any ambient mix of PM10-2.5 that is dominated by
rural windblown dust and soils and PM generated by agricultural and
mining sources. The EPA also proposed that agricultural sources, mining
sources and other similar sources of crustal material shall not be
subject to control in meeting the proposed standard. The EPA proposed
to set the new PM10-2.5 standard at a level of 70 [mu]g/
m3, continuing to provide a generally equivalent level of
protection against health effects associated with short-term exposure
(including hospital admissions for cardiopulmonary diseases, increased
respiratory symptoms and possibly premature mortality).
In addition, EPA proposed to revoke the annual PM10
standard everywhere, and the 24-hour PM10 standard
everywhere except in areas where there is at least one monitor that is
located in an urbanized area\1\ with a minimum population of 100,000
people and that violates the 24-hour PM10 standard based on
the most recent 3 years of data. This revocation of the PM10
standards would become effective upon promulgation of the
PM10-2.5 NAAQS (expected to be December 2006). In the
January 17, 2006, notice, the Agency provided a specific list of areas
where the 24-hour PM10 standard would not be revoked under
the proposal based on the most recent 3 years of data. EPA proposed to
revoke the 24-hour PM10 standard in all other areas. In
addition, EPA requested comment on whether the 24-hour PM10
standard should be retained in additional areas that are either
urbanized areas with populations less than 100,000 people or non-
urbanized areas (i.e., populations less than 50,000) but where the
majority of the ambient mix of PM10-2.5 is generated by high
density traffic on paved roads, industrial sources, and construction
sources, and which have at least one monitor that violated the 24-hour
PM10 standard based on the most recent 3 years of data.
---------------------------------------------------------------------------
\1\ As defined by the U.S. Bureau of the Census, an urbanized
area has ``a minimum residential population of at least 50,000
people'' and generally includes ``core census block groups or blocks
that have a population density of at least 1,000 people per square
mile and surrounding census blocks that have an overall density of
at least 500 people per square mile.'' The Census Bureau notes that
``under certain conditions, less densely settled territory may be
part of each UA.'' See https://www.census.gov/geo/www/ua/ua_2k.html.
---------------------------------------------------------------------------
For the secondary PM standards, EPA proposed to revise the current
standards by making them identical to the suite of proposed primary
standards for fine and coarse particles.
B. Revisions to Ambient Air Monitoring Regulations
At the same time EPA proposed revisions to the PM NAAQS, EPA also
proposed Revisions to the Ambient Air Monitoring Regulations (71 FR
2710, January 17, 2006) for criteria pollutants to support the proposed
revisions to the NAAQS. The proposal can be found at: https://
www.epa.gov/oar/particlepollution/actions.html. Included among the
proposed PM-related changes are new provisions to be added to 40 CFR
parts 53 and 58 which address approval of monitoring methods and
PM10-2.5 monitoring requirements. The added provisions in
part 53 would address approval of PM10-2.5 filter-based
Federal Reference Method (FRM) samplers and both filter-based and
continuous Federal Equivalent Method (FEM) monitors. Provisions in part
58 would provide the monitoring requirements for a PM10-2.5
network, including the minimum number of monitors a State must deploy.
In addition, the proposal adds provisions for the conditions under
which a PM10-2.5 monitor may be compared to the
PM10-2.5 NAAQS.
The proposal also amends a number of existing provisions for
PM2.5 monitoring, including changing the criteria for FEM
equivalency determinations for continuous PM2.5 monitors.
This should allow States to operate continuous monitors at more
required monitoring sites, thereby providing more robust data for the
PM2.5 air quality program.
C. Treatment of Data Influenced by Exceptional Events
The EPA will soon propose a rule to govern the review and handling
of air
[[Page 6721]]
quality monitoring data influenced by exceptional events. Section 319
of the Clean Air Act (CAA) defines an event as an exceptional event if
the event affects air quality; is not reasonably controllable or
preventable; is a natural event, or an event caused by human activity
that is unlikely to recur at a particular location; and is determined
by the Administrator to be an exceptional event. The EPA will be
proposing procedures and criteria related to the identification,
evaluation, interpretation and use of air quality monitoring data
related to the NAAQS where State air quality agencies petition EPA to
exclude, in whole or in part, air quality data that are directly
affected by exceptional events. Section 319 of the CAA, as amended by
section 6013 of the Safe Accountable Flexible Efficient-Transportation
Equity Act (SAFE-TEA) of 2005, requires EPA to publish a proposed rule
in the Federal Register, no later than March 1, 2006.
II. What Is EPA's Strategy for Addressing PM?
Our overall strategy for achieving the PM primary and secondary
standards is based on the structure outlined in the CAA. The CAA
outlines important roles for State and Tribal governments and for EPA
in implementing NAAQS.
States have primary responsibility for developing and implementing
SIPs that contain local and in-State measures needed to achieve the air
quality standards in each area. We assist States and Tribes by
providing technical tools, assistance and guidance, including
information on potential control measures. The EPA recently issued a
Proposed rule to Implement the Fine Particle NAAQS (70 FR 65984) to
support implementation of the 1997 PM2.5 NAAQS. In addition,
we set national emissions standards/limits for some sources, such as
new motor vehicles, certain categories of major new sources, and
existing stationary sources of toxic air pollutants, all of which may
obtain reductions in PM. Where upwind sources (such as coal-fired power
plants) significantly contribute to downwind problems in other States
or tribal areas, we can issue Federal regulations to ensure that the
upwind States address these contributing emissions (such as the Clean
Air Interstate Rule), or we can put in place Federal regulations in
situations where the upwind States fail to address these sources.
A. The State Implementation Plan (SIP) System
A SIP is the compilation of regulations and programs that a State
uses to carry out its responsibilities under the CAA, including the
attainment, maintenance, and enforcement of the NAAQS. States use the
SIP process to identify the emissions sources that contribute to the
nonattainment problem in a particular area, and to select the emissions
reductions measures most appropriate for that area, considering
technical and economic feasibility, and a variety of local factors such
as population exposure, enforceability, and economic impact. Under the
CAA, SIPs must ensure that areas reach attainment as expeditiously as
practicable. These plans take into consideration emissions reductions
resulting from national programs (such as mobile source regulations,
the acid rain program, or maximum achievable control technology (MACT)
standards for air toxics), as well as from State or local programs not
directly mandated under the CAA.
B. National Rules
As described in a recent EPA report, The Particle Pollution Report:
Current Understanding of Air Quality and Emissions through 2003,\2\
State and Federal programs have made substantial progress in reducing
ambient concentrations of PM10 and PM2.5. For
example, PM10 concentrations have decreased 31 percent
nationally since 1988. Regionally, PM10 concentrations
decreased most in areas with historically higher concentrations--the
Northwest (39 percent decline), the Southwest (33 percent decline), and
southern California (35 percent decline). Direct emissions of
PM10 have decreased approximately 25 percent nationally
since 1988.
---------------------------------------------------------------------------
\2\ Environmental Protection Agency (2004). The Particle
Pollution Report: Current Understanding of Air Quality and Emissions
through 2003. Office of Air Quality Planning and Standards;
Emissions, Monitoring, and Analysis Division, Research Triangle
Park, NC 27711; report no. EPA-454-R-04-002. December 2004.
---------------------------------------------------------------------------
Programs aimed at reducing direct emissions of particles have
played an important role in reducing PM10 concentrations,
particularly in western areas. Some examples of PM10
controls include paving unpaved roads and using best management
practices for agricultural sources of resuspended soil. Of the 87 areas
that were designated nonattainment for PM10 in the early
1990's, 64 now meet those standards. In cities that have not attained
the PM10 standards, the number of times the standard is
exceeded is down significantly.
National programs that affect regional emissions have contributed
to lower sulfate concentrations and, consequently, to lower
PM2.5 concentrations, particularly in the Industrial Midwest
and Southeast. National ozone-reduction programs designed to reduce
emissions of volatile organic compounds (VOCs) and nitrogen oxides
(NOX) also have helped reduce carbon and nitrate particles,
both of which are components of PM2.5. Power plant emissions
of sulfur dioxide dropped 33% from 1990 to 2003, largely as a result of
EPA's Acid Rain Program. Nationally, SO2 emissions have
declined 9 percent, NOX emissions have declined 9 percent,
and VOC emissions have declined by 12 percent from 1999 to 2003. In
eastern States affected by the Acid Rain Program, sulfates decreased 7
percent over the same period.
Over the next 10 to 20 years, national and regional regulations
will make major reductions in ambient PM2.5 levels. The
Clean Air Interstate Rule (CAIR) and the NOX SIP Call will
reduce SO2 and NOX emissions from electric
generating units and industrial boilers across the eastern half of the
U.S., regulations to implement the current ambient air quality
standards for PM2.5 will likely result in direct
PM2.5 and PM2.5 precursor controls in
nonattainment areas, and new national mobile source regulations
affecting off-highway diesel engines, highway gasoline and diesel
vehicles, and other mobile sources will reduce emissions of
NOX, direct PM2.5, SO2, and VOCs. The
EPA estimates that these Federal regulations for stationary and mobile
sources will cut SO2 emissions by 6 million tons annually in
2015 from 2001 levels. Emissions of NOX will be cut by 9
million tons annually in 2015 from 2001 levels. Emissions of VOCs will
drop by 3 million tons, and direct PM2.5 emissions will be
cut by 200,000 tons in 2015, compared to 2001 levels.
III. How Should EPA Implement the Transition From the 1997 PM2.5 NAAQS
to Any New 2006 PM2.5 NAAQS?
A. What Is the Status of Areas Designated Under the 1997 PM2.5 NAAQS?
On April 5, 2005, nonattainment designations became final for 39
nonattainment areas. These areas were designated based on air quality
data from 2001-2003 and 2002-2004. Nationally, PM2.5
concentrations have declined by 10 percent from 1999 to 2003.
Generally, PM2.5 concentrations have also declined the most
in regions with the highest concentrations--the Southeast (20 percent
decline), southern California (16 percent decline), and the
[[Page 6722]]
Midwest (9 percent decline)--with the exception of the Northeast, where
PM2.5 concentrations increased by 1%. Direct emissions of
PM2.5 have decreased by 5 percent nationally over the past 5
years.
Modeling done by EPA indicates that by 2010, 18 of the 39 areas
currently not attaining the 1997 PM2.5 standards should come
into attainment of those standards just based on regulatory programs
already in place, including CAIR, the Clean Diesel Rules, and other
Federal measures. Four more PM2.5 areas are projected to
attain the standards by 2015 based on the implementation of these
programs. All areas in the eastern U.S. will have lower
PM2.5 concentrations in 2015 relative to present-day
conditions. In most cases, the predicted improvement in
PM2.5 ranges from 10 percent to 20 percent.
B. How Might EPA Implement the Transition From the 1997 PM2.5 NAAQS to
Any New 2006 PM2.5 NAAQS?
The EPA has evaluated several options for the transition from the
1997 PM2.5 standards to any new 2006 PM2.5
standards, and is elaborating on two potential options. Should the
Agency decide to revise the current PM2.5 standards, then
either of the following two options would continue the momentum and
continuity of the existing implementation program as areas look to
reduce ambient PM2.5 concentrations to meet the current and
revised PM2.5 NAAQS. Any suggested alternatives to these
approaches should demonstrate how it will continue the momentum and
continuity of the implementation program.
1. PM2.5 NAAQS Option 1
Option 1 recognizes that the only proposed change to the 1997
annual PM2.5 standard is a change in the application of
spatial averaging (71 FR 2620). Because the EPA believes that the
proposed change, if adopted, would not be significant enough to require
new designations under section 107(d), we are soliciting comment on
whether it would be appropriate to view this revision as minor, thus
not requiring a designation process. Even though section 107(d) calls
for EPA to commence the designation process for ``any new or revised
NAAQS,'' exceptions could be made for revisions to a NAAQS of a de
minimis or insignificant nature such that they should not lead to the
initiation of the designation process and consequent establishment of
new SIP submission and attainment deadlines. Option 1 would be
considered only if EPA finalized a revision to the annual
PM2.5 standard that was of such a minor nature as the
proposed revision. It would not be available if EPA revised the
standard more substantially.
Following this path, EPA would propose not to revoke the 1997
annual PM2.5 standard, and would propose to revoke the 1997
24-hour PM2.5 standard 1 year after designations are
finalized under any new 2006 PM2.5 standard. With the
exception of 2 areas in California (South Coast Air Quality District
and San Joaquin Valley) all areas designated as nonattainment for
PM2.5 were only violating the annual standard. Under this
path, new nonattainment designations would only be made for the areas
which do not meet any new 2006 24-hour PM2.5 standard.
Therefore, areas which are designated nonattainment for the 1997 annual
PM2.5 standard would continue to develop and implement their
SIPs based on a final implementation rule for the PM2.5
NAAQS (proposed on November 1, 2005 at 70 FR 65984). Areas which are
newly designated nonattainment under any new 24-hour PM2.5
standard would submit a SIP by April 2013 following the proposed
schedule in part IV.C below. This approach would maintain the momentum
in the PM2.5 SIP development and implementation program. It
would also not require the development and implementation of an anti-
backsliding rule to maintain progress in the program, as no areas are
in nonattainment based solely on the 24-hour PM2.5 standard.
Therefore control measures would still be in place under the approved
PM2.5 SIPs.
2. PM2.5 NAAQS Option 2
Option 2 varies from Option 1 in that EPA would revoke the 1997
annual and 24-hour PM2.5 standards 1 year after designations
under any new 2006 PM2.5 standards. This approach is similar
to that promulgated under the ozone program (69 FR 23951, April 30,
2004) for the revocation of the 1-hour ozone standard one year after
designations under the 8-hour ozone standard. Following this path, EPA
would develop and implement an ``anti-backsliding'' rule to ensure that
SIP control measures developed and adopted under the 1997
PM2.5 NAAQS remained in place until SIPs could be submitted
and approved to meet any new 2006 PM2.5 standards. In the
anti-backsliding rule, EPA would address issues similar to those
addressed in the anti-backsliding rule adopted as part of the
transition from implementation of the 1-hour ozone standard to the 8-
hour ozone standard including: (1) Which planning and control
requirements should remain in effect; (2) effect of the revised
standards on the New Source Review (NSR) program; and (3) how the
transition would affect general and transportation conformity programs.
In addressing some of these issues, EPA is inclined to follow the
precedent set by the ozone program which required areas in
nonattainment with both the 1-hour and 8-hour ozone NAAQS to maintain
mandatory control measures already in place, and allowed such areas to
revise or remove discretionary control measures following a section
110(l) demonstration. In addition, such areas would implement
transportation conformity and NSR based on their designations for the
revised standard only, for the reasons explained in the ozone anti-
backsliding rule (69 FR 23954, April 30, 2004). The EPA invites comment
on these two options, and solicits comments on any additional options
which would ensure a smooth transition and continued improvement in air
quality.
IV. What Are the Potential Timelines for Implementation of Any New 2006
PM2.5 NAAQS?
A. How Would the Implementation Schedules of the 1997 PM2.5 NAAQS and
Any New 2006 PM2.5 NAAQS Fit Together if the Revised PM2.5 Standards
Are More Stringent Than the Current Standards?
Section 109(d)(1) of the CAA requires a thorough review of the
NAAQS, and revisions if appropriate, at 5-year intervals. Current
requirements of the CAA thus anticipate an overlap in review and
implementation of standards. The EPA believes that for planning
purposes, when EPA revises a standard as it has proposed to do, it is
beneficial for States to understand control strategies that may be
useful in attaining any new 2006 PM2.5 standards when developing
control strategies for the 1997 PM2.5 standards.
B. What Is EPA's Preferred Schedule for the Any New 2006 PM2.5
Designation Process?
Under the terms of the consent decree governing the review of the
1997 PM NAAQS, EPA agreed that no later than September 27, 2006, it
would sign for publication a notice of final rulemaking concerning its
review of the PM NAAQS. The EPA expects that any new 2006
PM2.5 standards would be published in the Federal Register
within 4 weeks, and become effective 60 days later probably in December
2006. Timeframes below are outlined based on this assumption. Section
107(d)(1) lays out a schedule allowing States up to 1 year in which to
make recommendations to EPA for areas that
[[Page 6723]]
might be designated as nonattainment for any new PM2.5
standards. State designation recommendations would then be due by
December 2007. Tribes would also be encouraged, but not required, to
submit designation recommendations to EPA for their reservations or
other areas under their jurisdiction by December 2007.
These recommendations would be based on 3 years of the most recent
monitoring data (e.g., 2004-2006). The EPA(s evaluation of the existing
PM2.5 monitoring network indicates that it is adequate for
designations under both the proposed revised annual and proposed
revised 24-hour standards. Depending on which revocation process is
selected for the 1997 PM2.5 NAAQS, designations may be for
the revised 24-hour standard alone or both the annual and 24-hour
standards.
Following submittal of designation recommendations by the States,
EPA would evaluate the recommendations and make possible modifications.
Consistent with section 107, States would be notified of these changes,
and would be allowed to make additional comments on the proposed
designations. The EPA would issue final PM2.5 designations
under any new PM2.5 NAAQS no later than December 2009. These
designations would be effective by April 2010. The CAA provides EPA
with up to 3 years to designate nonattainment areas following
promulgation of a new or revised NAAQS. The EPA anticipates that this
full time period may be necessary for a variety of reasons as it has
been in the past, including evaluating more recent data in order to
determine appropriate designation boundaries. This timeline would allow
States to look at 2006-2008 monitoring data and update their
recommendations to EPA if they choose to do so based on the more recent
data.
In addition, as was done for the 1997 PM2.5 NAAQS
designations, we would anticipate allowing a further update based on
2007-2009 monitoring data, and make designations effective in April
2010. Table 1 at the end of part IV(D) provides a timeline showing the
dates that would result from such a designation process. The EPA would
appreciate comments on this timeline and other potential approaches.
C. What Would the Schedule Be for Attainment Demonstrations and SIP
Submittals for Any New 2006 PM2.5 Standards?
Part D of title I of the CAA sets forth the requirements for SIPs
needed to attain the NAAQS. Part D includes a general subpart 1 which
applies to all NAAQS for which a specific subpart does not exist. These
provisions apply to the PM2.5 standards and would apply to
any revised PM2.5 standards. The EPA has currently proposed
implementation rules for PM2.5 (70 FR 65984) which, when
finalized, will govern any revised standards.
Section 172(b) of the CAA requires that at the time the Agency
promulgates nonattainment area designations, EPA must also establish a
schedule for States to submit SIPs meeting the applicable requirements
of section 172(c) and section 110(a)(2) of the CAA. Section 172(b)
requires that such schedule allow a State to submit its attainment
demonstration and SIP revision within no more than 3 years of
nonattainment designation. Following the above timeline (outlined in
IV.B), if nonattainment area designations become effective in April
2010, and EPA allows the maximum time for SIP submissions, then
attainment demonstrations and SIP revisions would be due by April 2013.
D. What Are Attainment Dates for Any New 2006 PM2.5 Standards?
Section 172(a)(2)(A) states that the attainment date for a
nonattainment area must be ``as expeditiously as practicable, but no
later than 5 years from the date of designation for the area.'' If any
new 2006 PM2.5 designations are made in December 2009 and
have an effective date of April 2010, the initial attainment date for
any new PM2.5 standard would be no later than April 2015. As
an aside, this attainment date would correspond with the latest date an
area designated in April 2005 could come into attainment with the 1997
PM2.5 NAAQS. For an area with a maximum 5-year attainment
date, EPA would determine whether it had attained the standard by
evaluating air quality data from the three previous calendar years
(2012-2014).
Section 172 also states that if EPA deems it appropriate, the
Agency may extend the attainment date for an area for a period not
greater than 10 years from the date of designation as nonattainment,
taking into account the severity of the nonattainment problem in the
area, and the availability and feasibility of pollution control
measures. For any area that is granted the full 5-year attainment date
extension, the attainment date would be as expeditiously as
practicable, but no later than April 2020. For such areas, EPA would
determine whether the area attained the standard by evaluating air
quality data from 2017, 2018, and 2019. Table 1 is an overview of the
proposed timeline for implementing any new 2006 PM2.5
standards.
Table 1.--Proposed Timeline for Any New 2006 PM2.5 Standards
------------------------------------------------------------------------
Effective date of standard December 2006
------------------------------------------------------------------------
Monitoring data used for State 2005-2007.
recommendations.
State recommendations to EPA....... December 2007.
Final designations signature....... December 2009.
Effective date of designations..... April 2010.
SIPs due........................... April 2013.
Attainment date.................... Up to April 2015 (based on 2012-
2014 data).
Attainment date with a 5-year Up to April 2020 (based on 2017-
extension. 2019 data).
------------------------------------------------------------------------
The EPA is soliciting comments on which relevant factors should
influence EPA's decision on any potential timeline.
V. What Are the Potential Timelines for Implementation of Any New PM10
2.5 NAAQS?
A. What Is a Potential Schedule for Any New PM10-2.5
Designation Process?
Section 107(d)(1)(B) gives the Agency the authority to promulgate
designations for all areas as expeditiously as practicable, but no
later than 3 years from the date of promulgation of the new or revised
NAAQS.
Currently, a PM10-2.5 monitoring network does not exist.
The EPA's proposed monitoring regulations for PM10-2.5 (71
FR 2710) call for monitors to be deployed by January 2009. If this
schedule is adopted, the first period
[[Page 6724]]
when 3 years of data would be available for State designation
recommendations would be mid-2012 based on air quality data for 2009-
2011. As noted above, following the statutory timeline, designations
for PM10-2.5 would be required to occur no later than late
2009. Three years of PM10-2.5 monitoring data will not be
available at that time. For EPA to meet its statutory obligation, EPA
would need to designate all areas as unclassifiable under section
107(d)(1)(A)(iii), on the basis that no information is available to
determine whether an area is meeting any new NAAQS for
PM10-2.5. From a historical perspective this was the
situation in 1997 when we established the PM2.5 NAAQS.
Subsequent, to the establishment of the PM2.5 NAAQS in 1997,
Congress passed legislation which modified the CAA for the purposes of
PM2.5 designations. EPA is potentially confronting this
issue again with respect to any new PM10-2.5 NAAQS. As a
policy, EPA does not think that designating all areas of the country as
unclassifiable provides useful information to the public about their
area meeting new air quality standards. EPA would prefer to not make
designations until three years of monitoring data is available. EPA is
soliciting comments on the best way to address this issue.
B. What Is EPA's Preferred Schedule for Designations for Any New PM10
2.5 Standards?
The first available 3 years of data from a monitoring network for
PM10-2.5 will be 2009-2011. If EPA had not previously
designated areas unclassifiable, EPA could then request recommendations
from States for areas that might be designated nonattainment for
PM10-2.5 by July 2012. This is approximately 6 months after
a full 3 years of data would be available for some areas. EPA believes
this is adequate time for evaluating and quality assuring data to make
recommendations on designations. On the other hand, States have until
May 1 to certify that their monitoring data is correct, and may need
additional time for designation recommendations. Another option would
be to allow the States until October 2012 to make recommendations. The
EPA would like to take comment on this option.
Following submittal of designation recommendations by the States,
EPA will evaluate the recommendations and make modifications by
December 2012. States will be notified of these changes, and given
another opportunity to comment on the proposed modifications to
designations. The EPA would then issue final modified
PM10-2.5 designations by May 2013 which would be effective
approximately July 2013.
If EPA had previously designated areas unclassifiable, then, once
EPA had sufficient monitoring data available, EPA would move forward in
accordance with the provisions of section 107(d)(3)(A) to notify States
that it believed designations for areas should be revised. States would
then have the opportunity to respond in accordance with section
107(d)(3)(B), and EPA would take action regarding any revisions of the
designations in accordance with section 107(d)(3)(C).
Since classifications under Title I are done at the same time as
designations, EPA is considering the role a classification system could
play in facilitating the implementation of any new PM2.5
NAAQS. The EPA prefers not to develop a classification system to use in
determining the amount of time permitted for attainment, for reasons
similar to those outlined in the Proposed Rule to Implement the Fine
Particle National Ambient Air Quality Standards; Proposed Rule (70 FR
page 66000, November 1, 2005). Developing a classification system is
only an option, not a requirement under section 172(a)(1), and for the
reasons noted EPA does not believe it would be preferable to implement
a classification scheme. The EPA would like comments on this potential
designation timeline, and on its intentions to not develop a
classification system.
C. What Is EPA's Preferred Schedule for Attainment Demonstrations and
SIP Submittals for Any New PM10 2.5 Standards?
Section 172(b) of the CAA requires EPA to establish a schedule for
a State to submit its attainment demonstration and SIP revision within
3 years of nonattainment designation. Following the schedule outlined
in part V(B) above, if nonattainment designations for any new
PM10-2.5 standards were effective in July 2013, then
attainment demonstrations and SIP revisions would be due by July 2016.
The EPA would like comments on this proposed timeline.
D. What Is EPA's Preferred Schedule for Attaining Any New PM10 2.5
Standards?
Section 172(a)(2)(A) states that the attainment date for a
nonattainment area must be ``as expeditiously as practicable, but no
later than 5 years from the date of designation for the area.'' If new
PM10-2.5 designations are made in May 2013 and are effective
in July 2013, the initial attainment date for PM10-2.5 would
be as expeditiously as practicable but no later than July 2018. For an
area with an attainment date of July 2018, EPA would determine whether
it had attained the PM10-2.5 standards by evaluating air
quality data from the 3 previous calendar years (i.e., 2015, 2016 and
2017).
Section 172 also states that if EPA deems it appropriate, the
Agency may extend the attainment date for an area for a period not
greater than 10 years from the date of designation, taking into account
the severity of the nonattainment problem in the area, and the
availability and feasibility of pollution control measures. For any
area that is granted the full 5-year attainment date extension, the
attainment date would be no later than July 2023. For such areas, EPA
would determine whether they have attained the standard by evaluating
air quality data from 2020, 2021 and 2022. Table 2 is an overview of
this proposed timeline for designation, SIP submittal and attainment
dates under this proposed schedule.
Table 2.--Proposed Timeline for a Possible 2006 PM10 2.5 Standards
------------------------------------------------------------------------
Effective date of standard December 2006
------------------------------------------------------------------------
Monitoring data used for State 2009-2011.
recommendations.
State recommendations to EPA....... July 2012.
Final designations signature....... May 2013.
Effective date of designations..... July 2013.
SIPs due........................... July 2016.
Attainment date.................... Up to July 2018 (based on 2015-2017
data).
Attainment date with extension..... Up to July 2023 (based on 2020-2022
data).
------------------------------------------------------------------------
[[Page 6725]]
The EPA requests comment on this potential timeline for attaining
any new PM10-2.5 standards.
VI. How Should EPA Implement the Transition From the PM10
Standards to Any New PM10-2.5 Standards?
A. What Is EPA's Proposal for Revoking the PM10 Standards?
Before areas are designated under any new PM10-2.5
standards, we intend to address how to transition from implementation
of the PM10 standards to any new PM10-2.5
standards. As part of the NAAQS proposal (71 FR 2620), EPA proposed to
revoke the annual PM10 standard everywhere, and the 24-hour
PM10 standard everywhere except in areas where there is at
least one monitor that is located in an urbanized area with a minimum
population of 100,000 people and that violates the 24-hour
PM10 standard based on the most recent 3 years of data. This
revocation would be effective upon promulgation of the PM NAAQS in
December 2006. The EPA also provided a list of places where the 24-hour
PM10 standard would not be revoked under the proposal. In
addition, EPA requested comment on whether the 24-hour PM10
standard should be retained in areas that are either urbanized areas
with populations less than 100,000 people or non-urbanized areas (i.e.,
population less than 50,000) but where the majority of the ambient mix
of PM10-2.5 is generated by high density traffic on paved
roads, industrial sources, and construction sources, and which have at
least one monitor that violated the 24-hour PM10 standard.
Comments on this revocation plan should be submitted under that notice
(71 FR 2620).
This raises a number of issues for those areas where the 24-hour
PM10 standard would still apply including: When and how
should the 24-hour PM10 standard be revoked for these areas;
should anti-backsliding provisions apply; how to address NSR and
maintenance issues; and other implementation issues. Our principal
objective for the transition is to ensure that air quality will not
degrade in areas where the potential new PM10-2.5 NAAQS
would apply, and that areas continue to make progress toward attainment
of the PM standards. Subject to requirements under the CAA for revising
SIPs, EPA expects States would take the opportunity to revise their
SIPs to reflect the revocation of the PM10 standards.
B. What Should the Timing Be for Revoking the 24-Hour PM10 Standard for
Those Areas Where the 24-Hour PM10 Standard Is Retained?
The EPA contemplates that the 24-hour PM10 standard
would be revoked one year after attainment/nonattainment designations
are effective for a 24-hour PM10-2.5 standard. Because
attainment/nonattainment designations would not occur until July 2013,
it is reasonable to expect that some areas where the 24-hour
PM10 standard has not been revoked would come into
attainment with the PM10 standard prior to July 2013. We
invite comment on how these areas should be treated.
C. What Transition Issues Are Created by Revoking the 24-Hour PM10
Standard in Areas Where It Is Currently Proposed To Be Retained and How
Might They Be Addressed?
1. Control Measures
EPA wants to ensure that air quality is not degraded if we move
from one version of the NAAQS to another. What protections should
remain in place to ensure that air quality will not degrade once the
24-hour PM10 standard is revoked, and that progress will
continue as areas transition from implementing the 24-hour
PM10 standard to implementing the 24-hour
PM10-2.5 standard?
a. What requirements based on an area's classification for the
PM10 standard should continue to apply?
The EPA believes an approach similar to what was done under the
ozone transition from the 1-hour to the 8-hour standard (69 FR 23951
page 23969) would be appropriate here in that control measures which
remain in place were determined by the area's classification. Such an
approach would mean that moderate PM10 nonattainment areas
should continue to require reasonably available control measures (RACM)
(as described in section 189(a)(1)(C) of the CAA). Serious
PM10 nonattainment areas should also continue to require
best available control measures (BACM) (section 189(b)(1)(B) of the
CAA). All nonattainment areas should have an EPA-approved part D SIP in
place, and continue to implement the nonattainment requirements and
control measures identified in the SIP. Any effort to change SIP-
approved measures would be subject to a section 110(l) demonstration of
no interference with applicable requirements.
The EPA also believes that those areas where the 24-hour
PM10 standard is being violated and has not been revoked
should continue to implement the requirements of the CAA until
nonattainment and attainment designations for PM10-2.5 are
completed. However, this could represent a significant period of time
(from 2006-2013). Consequently, EPA is interested in alternative views
regarding the appropriate implementation pathway for the
PM10 standard in these areas.
b. How should EPA address maintenance? Those PM10
nonattainment areas where the 24-hour PM10 standard has not
been revoked which come into attainment with the 24-hour
PM10 NAAQS prior to designations under the 24-hour
PM10-2.5 standard, may request to be redesignated as
attainment for PM10 under section 107(d). As such they would
need to submit a maintenance plan under section 175A. Maintenance areas
do not have any outstanding obligation to adopt further mandatory
control obligations. We would anticipate an approach to maintenance
requirements similar to what was provided in the ozone rule where
maintenance areas retain the discretion to modify any discretionary
control measures upon a demonstration under section 110(l) (69 FR 23951
page 23955). The EPA requests comments on how to address maintenance
areas.
2. Transportation Conformity
Transportation conformity is required under section 176(c) of the
CAA (42 U.S.C. 7506(c)) to ensure that federally supported highway and
transit project activities are consistent with (conform to) the purpose
of a SIP. Conformity to the purpose of a SIP means that transportation
activities will not cause new air quality violations, worsen existing
violations, or delay timely attainment of the NAAQS. Transportation
conformity applies in nonattainment areas and maintenance areas. The
EPA's transportation conformity rule, 40 CFR part 93, establishes the
criteria and procedures for determining whether transportation
activities conform to the State air quality plan. It also establishes
criteria and procedures for determining whether transportation
activities conform in areas where no SIP containing motor vehicle
emissions budgets yet exists.
Transportation conformity rulemakings, as well as other relevant
conformity materials such as guidance documents, policy memoranda, the
complete text of the conformity rule, and conformity research can be
found at EPA's transportation conformity Web site, at https://
www.epa.gov/otaq/transp.htm (once at the site, click on
``Transportation Conformity.''
[[Page 6726]]
Until areas are designated nonattainment, transportation conformity
will not apply for any new PM10-2.5 standard. Based on the
timeline outlined above, designations for any new PM10-2.5
NAAQS could be effective in July 2013, and for all nonattainment areas
transportation conformity would then apply 1 year later. Prior to the
designation date, EPA would propose to update the transportation
conformity rule to address any new PM10-2.5 standard.
The EPA will solicit public comment on these and other issues
associated with determining transportation conformity in any new
PM10-2.5 nonattainment areas when it proposes to revise the
conformity rule to address the new standard. Once we revoke the
PM10 standard and the associated designations,
transportation conformity will no longer apply under the terms of the
statute for that standard.
3. General Conformity
Section 176(c) of the CAA requires that before a Federal entity
takes an action, it must make a determination that the proposed action
will not interfere with the SIP or the State's ability to attain and
maintain the NAAQS. In November 1993, EPA promulgated two sets of
regulations to implement section 176(c). One set, known as the general
conformity regulations, deals with all other Federal activities besides
funding of highway and mass transit projects. These activities include
funding and approval of airport projects, expansion of military bases,
and permitting of projects to deepen waterways.
Federal agencies take thousands of actions every day and requiring
determinations on every action would not be possible. Therefore, EPA
established a number of exemptions to the rule requirements including a
de minimis emission level generally based upon the size of a major
stationary source in the nonattainment or maintenance area.
Following are a series of questions related to implementation of
general conformity on which EPA is soliciting input:
What de minimis levels should EPA establish for direct and
precursor emissions for any new PM10-2.5 standards? The EPA
currently does not have speciated monitoring data for
PM10-2.5. Consequently, we do not know if the mass of
PM10-2.5 contains a significant amount of particulate matter
formed by atmospheric chemical reactions.
In transitioning to a new standard, how should EPA treat
previous conformity evaluations and determinations based on the
PM10 standard?
Are there any categories of actions that should be exempt
from the conformity requirements for any new PM10-2.5
standards? If so, how could such exemptions be devised?
4. New Source Review Program
The NSR program is a preconstruction permitting program that
applies when a new source is constructed or an existing one is
modified. The major NSR program applies to major stationary sources and
is comprised of the Prevention of Significant Deterioration (PSD)
program that applies in attainment areas and a nonattainment NSR
program that applies to pollutants for which an area is designated
nonattainment.
There are many major NSR program implementation issues that EPA
will address for a new PM10-2.5 NAAQS, including revocation
of the existing PM10 NAAQS. In this ANPR, EPA is
highlighting some of the key issues and providing EPA's preliminary
thinking on approaches for addressing them. We recognize that there may
be other implementation issues not identified here, and we invite you
to identify them. When submitting comments, please support your
comments with adequate data and/or practical scenarios or
illustrations.
a. Does PM10 continue to be a regulated NSR pollutant
for PSD in areas where the 24-hour PM10 NAAQS would be
revoked?
The PSD program applies when a major stationary source of any
``regulated NSR pollutant'', that is located in an area designated as
attainment or unclassifiable for any criteria pollutant, is constructed
or undergoes a major modification (40 CFR 52.21(a)(2); 40 CFR
51.166(a)(7)). EPA defines a ``regulated NSR pollutant'' to include (1)
any pollutant for which a NAAQS has been promulgated (otherwise known
as a ``criteria'' pollutant); (2) any pollutant subject to a NewSource
Performance Standard promulgated under section 111 of the CAA; and (3)
any pollutant that is otherwise regulated under the Act, except for
hazardous air pollutants regulated under section 112 of the Act \3\ (40
CFR 52.21(b)(50); 40 CFR 51.166(b)(49)). Thus, in addition to applying
to criteria pollutants for which EPA has promulgated a NAAQS, the PSD
program also applies to any non-criteria pollutant that is covered by
the additional prongs of the definition of a ``regulated NSR
pollutant'' described above. However, not all of the PSD program
requirements outlined below are applicable to non-criteria pollutants
that are subject to the PSD program.
---------------------------------------------------------------------------
\3\ This definition also covers any pollutant that is subject to
any standard promulgated under or established by Title VI of the
Act, but this is not relevant to particulate matter.
---------------------------------------------------------------------------
The PSD requirements include but are not limited to:
Installation of Best Available Control Technology (BACT),
Air quality monitoring and modeling analyses to ensure
that a project's emissions will not cause or contribute to a violation
of any NAAQS or maximum allowable pollutant increase (PSD increment),
Notification of Federal Land Manager when a proposed
source or modification may affect nearby Class I areas, and
Public comment on the permit.
For any criteria pollutant subject to PSD, all PSD requirements
including the PSD increments analyses apply. However, since there are
no NAAQS for non-criteria pollutants, only some requirements, including
BACT, apply to these pollutants (See 42 U.S.C. 7475(a)(4); 40 CFR
52.21(j)); 40 CFR 52.166(j)).
The proposed revocation of the 24-hour PM10 NAAQS in
certain areas raises issues about whether existing PSD regulations
would continue to apply to PM10 in any respect after the
revocation of the NAAQS in these areas. The extent to which all or some
of the PSD requirements apply depends on whether PM10
continues to be a regulated NSR pollutant in these areas, either as a
criteria or a non-criteria pollutant, under EPA's regulations and the
CAA. We seek comment on the following options to address these issues:
Option 1. Since the 24-hour PM10 standard would remain
in effect at least in some areas, we could conclude that
PM10 continues to be a regulated NSR pollutant for the PSD
program. Thus, even in those areas in which the 24-hour PM10
NAAQS is revoked (24-hour revoked areas), PM10 would be
regarded as a regulated NSR pollutant only by virtue of being otherwise
subject to regulation under the CAA (40 CFR 52.21(b)(50)(iv)) because a
24-hour PM10 NAAQS continues to apply in other areas. Under
this approach, PSD for PM10 would continue to apply in all
areas. However, as stated earlier, only a few PSD requirements,
including BACT, would apply in 24-hour revoked areas since
PM10 would be regarded as a non-criteria pollutant in those
areas. In those areas where the 24-hour PM10 NAAQS is not
revoked, all PSD program elements would continue to apply for
[[Page 6727]]
PM10 because it remains a criteria pollutant in these areas.
Option 2. Alternatively, we could interpret all prongs of the
``regulated NSR pollutant'' definition to be area-specific. Thus, in
24-hour revoked areas, PM10 would no longer be a criteria
pollutant, and none of the other prongs of the definition of
``regulated NSR pollutant'' would apply to PM10 in these
areas. Therefore, none of the PSD requirements would apply to
PM10 in such areas. We request comment on whether there is
any other basis for retaining PM10 as a regulated NSR
pollutant, even if it is no longer a criteria pollutant.
b. Does the CAA require continued obligation for some form of PM
increment?
Section 163 of the CAA states that each SIP should contain measures
assuring that maximum allowable increases over baseline concentration
(increments) for PM shall not be exceeded in attainment areas. Section
163 contains specific numerical increments (expressed as [mu]g/m\3\)
for PM, which EPA initially implemented using the total suspended
particulate indicator. After EPA transitioned to PM10 as the
indicator for PM in 1987, the Agency substituted PM10
increments for the PM increments in section 163 based