The Treatment of Data Influenced by Exceptional Events, 12592-12610 [06-2179]
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Federal Register / Vol. 71, No. 47 / Friday, March 10, 2006 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 50 and 51
[EPA–HQ–OAR–2005–0159; FRL–8042–5]
RIN 2060–AN40
The Treatment of Data Influenced by
Exceptional Events
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
dsatterwhite on PROD1PC65 with PROPOSAL
AGENCY:
SUMMARY: Today, EPA is proposing a
rule to govern the review and handling
of air quality monitoring data
influenced by exceptional events.
Exceptional events are events for which
the normal planning and regulatory
process established by the Clean Air Act
(CAA) is not appropriate. In this
rulemaking action, EPA is proposing to:
Implement section 319(b)(3)(B) and
section 107(d)(3) authority to exclude
air quality monitoring data from
regulatory determinations related to
exceedances or violations of the
National Ambient Air Quality Standards
(NAAQS) and avoid designating an area
as nonattainment, redesignating an area
as nonattainment, or reclassifying an
existing nonattainment area to a higher
classification if a State adequately
demonstrates that an exceptional event
has caused an exceedance or violation
of a NAAQS. Also, EPA is proposing
four options with respect to whether,
and to what extent, States should be
required to take additional actions to
address public health impacts related to
the event.
DATES: Comments must be received on
or before May 9, 2006. Comments must
be postmarked by the last day of the
comment period.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2005–0159, by one of the
following methods:
• https://www.regulations.gov. Follow
the on-line instructions for submitting
comments.
• E-mail: Comments may be sent by
electronic mail (e-mail) to A–and–R–
Docket@epa.gov, Attention Docket ID
No. EPA–HQ–OAR–2005–0159.
• Fax: Fax your comments to: 202–
566–1741, Attention Docket ID no.
EPA–HQ–OAR–2005–0159.
• Mail: Send your comments to: Air
and Radiation Docket and Information
Center, U.S. Environmental Protection
Agency, Mail Code: 6102T, 1200
Pennsylvania Ave., NW., Washington,
DC 20460, Attention Docket ID No.
EPA–HQ–OAR–2005–0159.
• Hand Delivery: Air and Radiation
Docket and Information Center, U.S.
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Environmental Protection Agency, 1301
Constitution Avenue, NW., Room B102,
Washington, DC, Attention Docket ID
No. EPA–HQ–OAR–2005–0159. 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. EPA–HQ–OAR–2005–
0159. 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 information through https://
www.regulations.gov, or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means that 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 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. For additional instructions
on submitting comments, go to
SUPPLEMENTARY INFORMATION.
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 Office of Air and Radiation Docket
and Information Center, EPA West,
Room B102, 1301 Constitution Ave.,
NW., Washington, DC. The Public
Reading Room is open from 8:30 a.m. to
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4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Office of Air and
Radiation Docket and Information
Center is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT:
General questions concerning this
proposed rule should be addressed to
Mr. Larry D. Wallace, Ph.D., Office of
Air Quality Planning and Standards, Air
Quality Policy Division, Mail Code
C539–01, Research Triangle Park, NC
27711; telephone (919) 541–0906, and email address wallace.larry@epa.gov.
Questions concerning technical and
analytical issues related to this
proposed rule should be addressed to
Mr. Neil Frank, Office of Air Quality
Planning and Standards, Air Quality
Assessment Division, Mail Code C304–
04, Research Triangle Park, NC 27711;
telephone (919) 541–5560, and e-mail
address frank.neil@epa.gov.
SUPPLEMENTARY INFORMATION:
Public Hearing
The EPA will hold two public
hearings on today’s proposal during the
comment period. The details of the
public hearings, including the times,
dates, and locations will be provided in
a future Federal Register notice. The
public hearings will provide interested
parties the opportunity to present data,
views, or arguments concerning the
proposed rule. The EPA may ask
clarifying questions during the oral
presentations, but will not respond to
the presentations or comments at that
time. Written statements and supporting
information submitted during the
comment period will be considered
with the same weight as any oral
comments and supporting information
presented at the public hearings. Under
CAA section 307(d)(1)(A), the
procedural requirements of section
307(d) apply to this proposal. In
addition, under section 307(d)(1)(U), the
Administrator determines that this
action is subject to the provisions of
section 307(d). Section 307(d)(1)(U)
provides that the provisions of section
307(d) apply to ‘‘such other actions as
the Administrator may determine.’’ The
EPA is including the proposals in
today’s proposed rulemaking under
sections 307(d)(1)(A) and (U).
Comments
1. Submitting CBI. Do not submit this
information to EPA 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
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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.
2. Tips for Preparing Your Comments.
When submitting comments, remember
to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
• Follow directions—The agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your cost estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
In addition, please send a copy of
your comments to: Mr. Larry D. Wallace,
Ph.D., U.S. Environmental Protection
Agency, by one of the means listed
below:
1. E-Mail: wallace.larry@epa.gov.
2. Fax: (919) 541–5489, Attention: Mr.
Larry D. Wallace, Ph.D.
3. Mail: Mr. Larry D. Wallace, Ph.D.,
U.S. Environmental Protection Agency,
Office of Air Quality Planning and
Standards, Mail Code: C539–01,
Research Triangle Park, NC 27711.
4. Hand Delivery: Mr. Larry D.
Wallace, Ph.D., U.S. Environmental
Protection Agency, Office of Air Quality
Planning and Standards, 109 T.W.
Alexander Drive, Research Triangle
Park, NC 27709.
Table of Contents
The following is an outline of the
preamble.
I. Preamble Glossary of Terms and Acronyms
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II. Background and Purpose of Today’s
Rulemaking
A. Legislative Requirements
B. Historical Experience Concerning
Exceptional and Natural Events
III. Today’s Proposed Action
A. To Whom and to What Pollutants Does
Today’s Proposed Rule Apply?
B. How Does This Rule Relate to Indian
Tribes?
C. What Is an Exceptional Event?
D. Examples of Exceptional Events
1. Chemical Spills and Industrial
Accidents
2. Structural Fires
3. Exceedances Due to Transported
Pollution
4. Exceedances Due to a Terrorist Attack
5. Natural Events
a. Volcanic and Seismic Activities
b. Natural Disasters and Associated Cleanup Activities
c. High Wind Events
d. Unwanted Fires
e. Stratospheric Ozone Intrusions
IV. The Management of Air Quality Data
Affected by Exceptional Events
A. Flagging of Data in the AQS Database
B. What Does It Mean for an Event To
‘‘Affect Air Quality’’?
1. Option 1: 95th Percentile Criterion
2. Option 2: 75th Percentile/95th Percentile
Tiered Approach
3. Option 3: Case-by-Case Approach Based
On Weight of Evidence
C. Use of a ‘‘But For’’ Test
D. Schedules and Procedures for Flagging
and Requesting Exclusion of Data
1. Option 1: Early Data Flagging and
Demonstration Submission
2. Option 2: Early Data Flagging and
Delayed Demonstration Submission
3. Option 3: Delayed Data Flagging and
Demonstration Submission
E. Exclusion of Entire 24-Hour Value as
Opposed to a Partial Adjustment of the
24-Hour Value
F. What Should States be Required To
Submit in Their Exceptional Events
Demonstrations?
G. Special Considerations Relevant to
Proposed Standards for PM10–2.5
H. Public Availability of Air Quality Data
and Demonstrations Related to
Exceptional Events
V. Additional Requirements
A. Option 1: Proposed Option: Require
Public Notification, Education and
Appropriate and Reasonable Measures
B. Option 2: The Development of a
Mitigation Plan by States Under Section
110 of the CAA
C. Option 3: The Development of a
Mitigation Plan for Episodic Events
D. Option 4: Do Not Require States To
Adopt and Implement Specific
Mitigation Plans or Measures Under This
Rule
VI. Special Treatment of Certain Events
Under This Rule
A. Volcanic and Seismic Activities
B. High Wind Events
C. Stratospheric Ozone Intrusion
VII. Treatment of Fireworks Displays
VIII. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
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B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions that
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer
Advancement Act
I. Preamble Glossary of Terms and
Acronyms
The following are abbreviations of
terms used in the preamble.
AQS Air Quality System
BACM Best Available Control
Measures
CAA Clean Air Act
CAAA Clean Air Act Amendments
EPA Environmental Protection Agency
FIP Federal Implementation Plan
FMP Fire Mitigation Plan
NAAQS National Ambient Air Quality
Standards
NEAP Natural Event Action Plan
OAQPS Office of Air Quality Planning
and Standards
PM10 Particles with a nominal mean
aerodynamic diameter less than or
equal to 10 micrometers
PM10–2.5 Particles with a nominal
mean aerodynamic diameter greater
than 2.5 micrometers and less than or
equal to 10 micrometers
PM2.5 Particles with a nominal mean
aerodynamic diameter less than or
equal to 2.5 micrometers
RACM Reasonably Available Control
Measures
SIP State Implementation Plan
SAFE–TEA–LU Safe Accountable
Flexible Efficient-Transportation
Equity Act—A Legacy for Users
SMP Smoke Management Plan
TAR Tribal Authority Rule
TIP Tribal Implementation Plan
II. Background and Purpose of Today’s
Rulemaking
A. Legislative Requirements
Today, EPA is proposing a rule to
govern the review and handling of air
quality monitoring data influenced by
exceptional events. As discussed below,
these are events for which the normal
planning and regulatory process
established by the CAA is not
appropriate. Section 319 of the CAA, as
amended by section 6013 of the Safe
Accountable Flexible EfficientTransportation Equity Act: A Legacy for
Users (SAFE–TEA–LU) of 2005, requires
EPA to publish this rule in the Federal
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Register no later than March 1, 2006.1
Further, EPA is required to issue the
final rule no later than 1 year from the
date of proposal.
The EPA is proposing to establish
procedures and criteria related to the
identification, evaluation,
interpretation, and use of air quality
monitoring data related to any NAAQS
where States petition EPA to exclude
data that are affected by exceptional
events. Section 319 defines an event as
an exceptional event if the event affects
air quality; 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 statutory
definition of exceptional event
specifically excludes stagnation of air
masses or meteorological inversions; a
meteorological event involving high
temperature or lack of precipitation; or
air pollution relating to source
noncompliance.
Section 319(b)(3)(B)(i) requires a State
air quality agency to demonstrate
through ‘‘reliable, accurate data that is
promptly produced’’ that an exceptional
event occurred.2 Section 319(b)(3)(B)(ii)
requires that ‘‘a clear causal
relationship’’ be established between a
measured exceedance of a NAAQS and
the exceptional event demonstrating
‘‘that the exceptional event caused a
specific air pollution concentration at a
particular location.’’ In addition, section
319(b)(3)(B)(iii) requires a public
process to determine whether an event
is an exceptional event. Finally, section
319(b)(3)(B)(iv) requires criteria and
procedures for a Governor to petition
the Administrator to exclude air quality
monitoring data that is directly due to
exceptional events from use in
determinations with respect to
exceedences or violations of the
NAAQS.
Section 319 also contains a set of five
principles for EPA to follow in
developing regulations to implement
section 319:
(i) Protection of public health is the
highest priority;
(ii) Timely information should be
provided to the public in any case in
which the air quality is unhealthy;
(iii) All ambient air quality data
should be included in a timely manner
1 All subsequent references to section 319 of the
CAA in this proposal are to section 319 as amended
by SAFE–TEA–LU unless otherwise noted.
2 While this document refers primarily to States
as the entity responsible for flagging data impacted
by exceptional events, other agencies, such as local
or Tribal government agencies, may also have
standing to flag data as being affected by these types
of events, and the criteria and procedures that are
discussed in this rulemaking also apply to these
entities.
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in an appropriate Federal air quality
data base that is accessible to the public;
(iv) Each State must take necessary
measures to safeguard public health
regardless of the source of the air
pollution; and
(v) Air quality data should be
carefully screened to ensure that events
not likely to recur are represented
accurately in all monitoring data and
analyses (42 U.S.C. 7619(b)(3)(A)).
In adopting revisions to section 319,
EPA believes that Congress sought to
provide statutory relief to States to
allow them to avoid being designated as
nonattainment or to avoid continuing to
be designated nonattainment as a result
of exceptional events in appropriate
circumstances. In addition, Congress
indicated that States should not have to
prepare and implement regulatory
strategies when their air quality is
affected by events beyond their
reasonable control. To accomplish this
goal, Congress enumerated certain
minimum requirements for this
rulemaking. In addition, Congress
provided certain statutory principles for
EPA to follow in promulgating
regulations to exclude data affected by
exceptional events.
Section 319 also includes an interim
provision, section 319(b)(4), that
addresses the transition period between
the present and the date that a final
regulation governing the treatment of
data related to exceptional events is
promulgated. The provision indicates
that following EPA guidance documents
continues to apply until the effective
date of a final regulation promulgated
under section 319(b)(2): ‘‘Guidance on
the Identification and Use of Air Quality
Data Affected by Exceptional Events’’
(July 1986); ‘‘Areas Affected by PM10
Natural Events,’’ May 30, 1996; and
appendices I, K, and N to 40 CFR part
50, which describe how air quality
monitoring data are to be used and
interpreted to determine compliance
with the applicable NAAQS. The statute
requires the promulgation of the final
rule no later than 1 year following the
publication of this proposed rule.
Quality Standards,’’ Guideline No. 1.2–
008 (revised February 1977).3
In July 1986, EPA issued the guidance
entitled, ‘‘Guideline on the
Identification and Use of Air Quality
Data Affected by Exceptional Events’’
(the Exceptional Events Policy). The
Exceptional Events Policy provided
criteria for States to use in making
decisions related to identifying data that
have been influenced by an exceptional
event.
In addition to the Exceptional Events
Policy, on July 1, 1987, EPA
promulgated the NAAQS for PM10
(particulate matter with an aerodynamic
diameter of 10 micrometers or less)
which also addressed the issue of
excluding or discounting data affected
by exceptional events.4 Appendix K of
that rule allows for special
consideration of data determined to be
affected by an exceptional event.
Section 2.4 of appendix K authorizes
EPA to discount from consideration in
making attainment or nonattainment
determinations for air quality data that
are attributable to ‘‘an uncontrollable
event caused by natural sources’’ of
PM10, or ‘‘an event that is not expected
to recur at a given location.’’ Section 2.4
of appendix K, together with EPA
guidance contained in the Exceptional
Events Policy, describes the steps that
should be taken for flagging PM10 data
that a State believes are affected by an
exceptional or natural event.
In 1990, section 188(f) was added to
the CAA. This section of the CAA
provided EPA authority to waive either
a specific attainment date or certain
planning requirements for serious PM10
nonattainment areas that were affected
by nonanthropogenic sources. In
response to section 188(f), and in
consideration of the CAA consequences
for areas affected by elevated
concentrations caused by natural events,
in 1996 EPA issued a policy to address
data affected by natural events entitled,
‘‘Areas Affected by PM10 Natural
Events,’’ (the PM10 Natural Events
Policy).5
B. Historical Experience Concerning
Exceptional and Natural Events
3 ‘‘Guideline for Interpretation of Air Quality
Standards,’’ U.S. Environmental Protection Agency,
Office of Air Quality Planning and Standards,
Research Triangle Park, N.C. OAQPS No. 1.2–008
(Revised February 1977). The guidance indicated
the need for a data flagging system which would
require the submittal of detailed information
establishing that a violation was due to
uncontrollable natural sources and that the
information could be used in decision-making
related to the feasibility of modifying control
strategies.
4 Federal Register (52 FR 24667), July 1, 1987.
5 Memorandum from Mary D. Nichols, Assistant
Administrator for Air and Radiation, to EPA
Regional Offices entitled, ‘‘Areas Affected by PM10
Natural Events,’’ May 30, 1996.
Since 1977, EPA guidance and
regulations have either implied or
documented the need for a flagging
system for data affected by an
exceptional event. The first EPA
guidance related to the exclusion or
discounting of data affected by an
exceptional event was an Office of Air
Quality Planning and Standards
(OAQPS) guidance document entitled,
‘‘Guidelines for the Interpretation of Air
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On July 18, 1997, EPA issued revised
NAAQS for ozone and a new NAAQS
addressing PM2.5. For ozone, the revised
NAAQS provided for an 8-hour
averaging period (versus 1 hour for the
previous NAAQS), and the level of the
standard was changed from 0.12 ppm to
0.08 ppm (62 FR 38856). For the PM2.5
NAAQS, EPA established both a new
24-hour standard and a new annual
standard. In that Federal Register, EPA
also promulgated appendices I and N to
40 CFR part 50. Appendices I and N
provided the methodologies for
determining whether an area is in
attainment of the 8-hour ozone and
PM2.5 NAAQS respectively, using
ambient air quality data. Section 1.0 of
appendix I, and section 1.0(b) of
appendix N provide the authority for
EPA to give special consideration to
data determined to be affected by an
exceptional or natural event.
Appendices K, I, and N, which are a
part of the NAAQS for the affected
pollutants as described above, provide
that, while States must submit all valid
ambient air quality data to EPA’s Air
Quality System (AQS) data base for use
in making regulatory decisions, in some
cases it may be appropriate for the
Regional Administrator to exclude,
discount, weight, or make adjustments
to data that have been appropriately
flagged from calculations in determining
whether or not an area has attained the
standard. These decisions are to be
made on a case-by-case basis using all
available information related to the
event in question, and are required to be
made available to the public for review.
It should also be noted that, while it
would be desirable to be able to adjust
the daily value to exclude only those
portions of the data that are attributable
to the exceptional event, due to
technical limitations, such subtraction
has not been possible, and EPA’s
historical practice has been to exclude
a daily measured value in its entirety
when that value is found to be largely
caused by an exceptional event.
Following the promulgation of the 8hour ozone and the PM2.5 NAAQS, EPA
provided additional guidance to States
on how to address data affected by
exceptional and natural events.6 That
guidance directed the States to follow
three specific EPA guidance documents
6 ‘‘Guideline on Data Handling Conventions for
the PM NAAQS,’’ United States Environmental
Protection Agency, Office of Air Quality Planning
and Standards, Research Triangle Park, N.C. 27711,
EPA–454/R–99–008, April 1999.
‘‘Guideline on Data Handling Conventions for the
8-hour Ozone NAAQS,’’ United States
Environmental Protection Agency, Office of Air
Quality Planning and Standards, Research Triangle
Park, N.C. 27711, EPA–454/R–99–008, April 1999.
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in making determinations related to data
influenced by exceptional and natural
events: (1) The Exceptional Events
Policy; (2) The PM10 Natural Events
Policy; and (3) The Interim Air Quality
Policy on Wildland and Prescribed
Fires, Memorandum from Richard D.
Wilson, Acting Assistant Administrator
for Air and Radiation, to EPA Regional
Administrators, May 15, 1998. The
Interim Air Quality Policy on Wildland
and Prescribed Fires addressed the
treatment of air quality monitoring data
that are affected by wildland and
prescribed fires that are managed for
resource benefits.7 The EPA will
continue to use these policies to address
issues related to the existing and/or
revised PM2.5 NAAQS pending EPA’s
final action on today’s proposed
rulemaking. Similarly, issues related to
exceptional and natural events affecting
the ozone standard will continue to be
addressed under the 1986 Exceptional
Events Policy until EPA issues a final
exceptional events rule.
III. Today’s Proposed Action
A. To Whom and to What Pollutants
Does Today’s Proposed Rule Apply?
Under the statutory scheme
established by the CAA, States are
primarily responsible for the
administration of air quality
management programs within their
borders. This includes the monitoring
and analysis of ambient air quality and
submission of monitoring data to EPA,
which are then stored in EPA’s AQS
data base. The EPA retains an important
oversight responsibility for ensuring
compliance with CAA requirements.
With respect to the treatment of air
quality monitoring data, States are
responsible for ensuring data quality
and validity and for identifying
measurements that they believe warrant
special consideration, while EPA is
responsible for reviewing and approving
or disapproving any requests for such
consideration. Therefore, if adopted,
today’s proposed rule would apply to all
States; to local air quality agencies to
whom a State has delegated relevant
responsibilities for air quality
management, including air quality
monitoring and data analysis; and, as
discussed below, to Tribal air quality
agencies where appropriate. This
proposed rule would also govern EPA’s
actions in reviewing and approving or
disapproving the relevant actions taken
7 Following the promulgation of this rule, EPA
will revise the ‘‘Interim Air Quality Policy on
Wildland and Prescribed Fires’’ to be consistent
with current policies related to wildland and
prescribed fires as well as the final rulemaking on
exceptional events.
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or requested by States. Where EPA
implements air quality management
programs on Tribal lands, this proposed
rule would govern those actions as well.
At present, only the NAAQS for ozone
and PM contain provisions which allow
for the special handling of air quality
data affected by exceptional events (40
CFR part 50, appendices K, I, and N).
The language of section 319 of the CAA
is broad in terms of making its
provisions applicable to events that
‘‘affect air quality’’ and to exceedances
or violations of ‘‘the national ambient
air quality standards’’ (42 U.S.C.
7619(b)(1)(A)(i), (b)(3)(B)(iv)). Thus, its
provisions can apply to the NAAQS for
any criteria pollutant. Because the
NAAQS established for other criteria
pollutants do not currently contain
provisions permitting the discounting or
exclusion of data due to exceptional
events, we are proposing to only apply
the provisions of this rule initially to
ozone and PM. As we review and
consider the need for revisions to the
NAAQS for other pollutants, we will
include provisions to address
exceptional events in those NAAQS in
accordance with section 319, as
appropriate at that time. Because
issuance of a new or revised NAAQS
will necessitate the initiation of the
designation process, EPA believes that
the NAAQS rules are an appropriate
place to make provision for exceptional
events in the evaluation of air quality
data. In the interim, where exceptional
events result in exceedances or
violations of NAAQS that do not
currently provide for special treatment
of the data, we intend to use our
discretion as outlined under section
107(d)(3) not to redesignate affected
areas as nonattainment based on these
events.
B. How Does This Rule Relate to Indian
Tribes?
Under the CAA and the Tribal
Authority Rule (TAR), eligible Indian
Tribes may develop and submit Tribal
Implementation Plans (TIPs) for EPA
approval, to administer requirements
under the CAA on their reservations and
other areas under their jurisdiction.
However, Tribes are not required to
develop TIPs or otherwise implement
relevant programs under the CAA. The
EPA has stated that it will continue to
ensure the protection of air quality
throughout the nation, including in
Indian country, and will issue Federal
Implementation Plans (FIPs) as
necessary or appropriate to fill gaps in
program implementation in affected
areas of Indian country (63 FR 7254,
7265; February 12, 1998).
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In cases where a Tribal air quality
agency has implemented an air quality
monitoring network which is affected by
emissions from exceptional events, the
criteria and procedures identified in this
proposed rule may be used to exclude
or discount data for regulatory purposes.
Certain Tribes may implement all
relevant components of an air quality
program for purposes of meeting the
various requirements of this proposed
rule. In some cases, however, a Tribe
may implement only portions of the
relevant program and may not be in a
position to address each of the
procedures and requirements associated
with excluding or discounting
emissions data (e.g., a particular Tribe
may operate a monitoring network for
purposes of gathering and identifying
appropriate data, but may not
implement relevant programs for the
purpose of mitigating the effects of
exceptional events required under this
proposed rule). The EPA intends to
work with Tribes on the implementation
of this proposed rule, which may
include appropriate implementation by
EPA of program elements ensuring that
any exclusion or discounting of data in
Indian country areas with air quality
affected by exceptional events comports
with the procedures and requirements
of this proposed rule.
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C. What Is an Exceptional Event?
In accordance with the language in
section 319, EPA is proposing to define
the term ‘‘exceptional event’’ to mean an
event that:
(i) Affects air quality;
(ii) Is not reasonably controllable or
preventable;
(iii) Is an event caused by human
activity that is unlikely to recur at a
particular location or a natural event;
and
(iv) Is determined by the
Administrator through the process
established in these regulations to be an
exceptional event.
It is important to note that natural
events, which are one form of
exceptional events according to this
definition, may recur, sometimes
frequently (e.g., western wildfires). For
purposes of this rule, EPA is proposing
to define ‘‘natural event’’ as an event in
which human activity has no substantial
or direct causal connection to the event
in question. We recognize that over
time, certain human activities may have
had some impact on the conditions
which later give rise to a ‘‘natural’’ air
pollution event. However, we do not
believe that small historical human
contributions should preclude an event
from being deemed ‘‘natural.’’
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In this proposed rule, EPA also
defines the term ‘‘exceedance’’ with
respect to compliance with the NAAQS
and establishes criteria for determining
when an event can be said to ‘‘affect air
quality.’’ We are not proposing more
detailed requirements for determining
when an event is ‘‘not reasonably
controllable or preventable’’ because we
believe that such determinations will
necessarily be dependent on specific
facts and circumstances that cannot be
prescribed by rule. In adopting section
188(f) of subpart 4 of the 1990
amendments to the CAA, Congress
recognized and provided for
distinctions between these types of
activities, while discussing
circumstances under which events
should or should not be considered
natural (see Public Law 101–549, CAA
Amendments of 1990 House Report No.
101–290(l), May 17, 1990; and
discussion of Mono Lake, California
therein).
D. Examples of Exceptional Events
The EPA believes that the following
types of events meet the definition of
exceptional events, as defined above.
This means that air quality data affected
by these types of events may qualify for
exclusion under this proposed rule if all
other requirements of the rule are met.
The AQS data base also contains a more
detailed list of other similar events that
may be flagged for special consideration
(https://www.epa.gov/ttn/airs/airsaqs/
manuals/ codedescs.htm).
1. Chemical Spills and Industrial
Accidents
Emissions that result from accidents
such as fires, explosions, power outages,
train derailments, vehicular accidents,
or combinations of these may be flagged
as an exceptional event.
2. Structural Fires
Structural fires include any accidental
fire involving a manmade structure.
3. Exceedances Due to Transported
Pollution
Transported pollution, whether
national or international in origin and
whether from natural or anthropogenic
sources, may cause exceedances which
are eligible for exclusion under this rule
as long as the other criteria and
requirements for exceptional events
under this rule are met. For example,
States may flag, and EPA may exclude,
data associated with fires occurring
outside of the borders of the United
States, such as forest fires in Mexico,
Central America, and Canada; or
transport events such as African dust
and Asian dust which contribute
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significantly to ambient concentrations
of a pollutant, leading to exceedances or
violations of the NAAQS. An example
of interstate transported emissions
which may be flagged as due to an
exceptional event would be emissions
due to smoke from wildland fires which
cause exceedances or violations at
monitoring sites in other States. Other
types of events may be considered on a
case-by-case basis.
4. Exceedances Due to a Terrorist Attack
Emissions that result from a terrorist
attack such as smoke from fires, dust,
explosions, power outages, train
derailments, vehicular accidents, or
combinations of these may be flagged as
an exceptional event.
5. Natural Events
The natural events addressed by this
proposed rule are: (1) Volcanic and
seismic activities; (2) natural disasters
and associated cleanup activities; (3)
high wind events; (4) unwanted fires;
and (5) stratospheric ozone intrusions.
The EPA will consider other types of
natural events on a case-by-case basis.
a. Volcanic and Seismic Activities.
Ambient concentrations of particulate
matter for which volcanic eruptions or
seismic activity caused or contributed to
high levels of particulate matter in an
affected area will be treated as natural
events. While not occurring frequently,
volcanic and seismic activity can affect
air quality data related to the particulate
matter NAAQS for an extended period
of time after an event. Volcanic
eruptions contribute to ambient
concentrations in two ways;
concentrations due to primary
emissions (e.g., ash); and emissions of
precursor pollutants (e.g., sulfur
dioxide) that contribute to the
secondary formation of particulate
matter. Seismic activity (e.g.,
earthquakes) can also contribute to
ambient particulate matter
concentrations by shaking the ground,
causing structures to collapse and
otherwise raising dust.
b. Natural Disasters and Associated
Clean-up Activities. For the purpose of
flagging, major natural disasters, such as
hurricanes and tornados for which
State, local, or Federal relief has been
granted, and clean-up activities
associated with these events may be
considered exceptional events.
c. High Wind Events. High wind
events are events that affect ambient
particulate matter concentrations
through re-entrainment of material, i.e.,
by raising dust. Concentrations of coarse
particles, i.e., PM10–2.5 and PM10 in some
locations, are most likely affected by
these types of events, although PM2.5
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standards may be exceeded under such
circumstances as well.
d. Unwanted Fires. Ambient
particulate matter concentrations caused
by smoke from wildland fires will be
treated as due to natural events if the
fires are determined to be unwanted
fires, designated wildland fire use fires,
not designated or managed as prescribed
fires, or requiring appropriate
suppression action by a wildland
manager.8
The question of what is a natural
versus an anthropogenic fire has
particular significance in considering
the impacts of wildland fires on air
quality and how they should be
regarded under today’s proposed rule.
Federal land managers have given
recognition to several different types of
wildland fires, depending on their
causal circumstances and the role that
such fires play in the affected
ecosystems. ‘‘Wildfires’’ are described
as unplanned, unwanted wildland fires,
and include unauthorized burns (such
as arson or acts of carelessness by
campers), prescribed burns that escape
control due to unforeseen
circumstances, or other wildland fires
where the primary objective is to
suppress the fire as quickly as possible.
In contrast, ‘‘wildland fire use’’ fires
are those which were ignited naturally
or unintentionally (e.g., as the result of
lightning) and are allowed to continue
burning without suppression efforts in
locations that have been designated in
fire management plans as areas where
fires are necessary and desirable to
accomplish specific resource
management objectives. ‘‘Prescribed
fires’’ are those ignited purposely to
accomplish specific management
objectives, and have been subject to
written, approved prescribed fire plans
(‘‘Interagency Strategy for Directives
Task Group,’’ Memorandum from
National Fire and Aviation Executive
Board to Agency Personnel: Bureau of
Indian Affairs, Bureau of Land
Management, National Park Service,
U.S. Fish and Wildlife Service, USDA
Forest Service, April 18, 2005). Under
these classifications, we believe that
wildfires due to whatever causes them
clearly fall within the meaning of
‘‘natural events’’ as that term is used in
section 319. Similarly, we believe that
wildland fire use fires qualify as
‘‘natural events’’ by virtue of their
natural origins.
Prescribed fires, however, cannot be
classified as ‘‘natural,’’ given their
8 It should be noted that this rule does not cover
agricultural burning. To the extent that it is
necessary for EPA to address this issue, we will do
so in the future via separate guidance or
rulemaking.
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clearly anthropogenic origins.
Nonetheless, we believe that prescribed
fires are not automatically excluded
from the definition of exceptional
events. If a prescribed fire meets the
statutory criteria of being ‘‘unlikely to
recur at the same location’’ or ‘‘not
reasonably controllable or preventable,’’
and the measures specified below, it
may qualify as an exceptional event.
Prescribed fires carried out for
resource management objectives are
frequently designed to restore the role of
wildland fires as they once occurred
under natural conditions. As such, their
expected frequency can vary widely,
depending on the fire regenerative cycle
of a particular landscape or wildland
ecosystem. The natural fire cycle can
range from once every year to less
frequently than once in 35–60 years.
Thus in many, though not all, cases it
may be demonstrated that the likelihood
of recurrence is sufficiently small that
these events should be accorded special
consideration under the rule.
Since a prescribed fire is being
deliberately ignited, it does not qualify
as ‘‘natural,’’ and one view is that it
cannot qualify as ‘‘not reasonably
controllable or preventable.’’ However, a
different interpretation of this provision
of section 319 examines whether there
are any reasonable alternatives to the
use of fire in light of the needs and
objectives to be served by it. For
instance, there may be a sufficient
build-up of forest fuels in a particular
area that if left unaddressed would pose
an unacceptable risk of catastrophic
wildfire, which result in adverse
impacts of much greater magnitude and
severity than would result from the
careful use of prescribed fires. A
particular ecosystem may also be highly
dependent on a natural fire cycle to
maintain a sustainable natural species
composition. Alternatively, pest or
disease outbreaks in an area may be
such that there are no reasonable
alternatives to fire. In some cases, other
legal requirements may preclude the use
of mechanical fuel reduction methods
such as in designated wilderness or
National Parks. Where such ecological
conditions exist, or where mechanical
or other treatments are not reasonably
feasible for reasons that include, but are
not limited to, a lack of access or severe
topography, we believe that it would be
appropriate to exclude the impacts from
well-managed prescribed fires to
address them. Well-managed prescribed
fires are those that consider smoke
impacts prior to and during the burn,
barring unforeseen circumstances, and
when the prescribed fire is in
compliance with a Smoke Management
Plan (SMP).
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The EPA is proposing in this action
that States continue to follow the smoke
management provisions described in the
‘‘Interim Air Quality Policy on Wildland
and Prescribed Fires,’’ issued May 15,
1998 (Wildland and Prescribed Fire
Policy). This policy provides that EPA
will allow exceedances to be discounted
that have been flagged by a State as
having been caused by prescribed fires
used for purposes of resource
management provided that the State
certifies that it has adopted and is
implementing a certified SMP as
described in our policy. Under our
proposal, if a State, local, or Tribal air
quality agency does not certify that a
basic SMP is being implemented, or that
basic smoke management practices are
being employed by burners, EPA would
not exclude data related to exceedances
or violations attributed to prescribed
fires managed for resource benefits.
We request comments on the
interpretation of prescribed fire
described above on the proposed
requirements for SMPs, and on any
additional criteria or conditions that
should be considered in determining
whether and under what circumstances
prescribed fires should be considered to
be exceptional events.
e. Stratospheric Ozone Intrusions.
Stratospheric ozone intrusion is
considered to be a natural event. A
stratospheric ozone intrusion occurs
when a parcel of air originating in the
stratosphere, which is at an average
height of 20 km or 12.4 miles, is reentrained directly to the surface of the
earth. Stratospheric ozone intrusions are
very infrequent, localized events of
short duration. They are typically
associated with strong frontal passages
and, thus, may occur primarily during
the spring season.
IV. The Management of Air Quality
Data Affected by Exceptional Events
The EPA is proposing that, in order to
exclude air quality data from
consideration for regulatory purposes,
States must follow the procedures,
timelines, and other requirements
described in this proposed rule.
Specifically, States must clearly
identify, or ‘‘flag,’’ data they believe to
be influenced by such events; they must
show that they have flagged days on
which air quality has been ‘‘affected’’ by
exceptional events according to EPA
criteria; and they must submit
appropriate documentation
demonstrating that the exceptional
event caused the exceedance or
violation of the NAAQS in question.
Each of these steps is described in detail
below.
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A. Flagging of Data in the AQS Data
Base
Air quality data are required,
pursuant to 40 CFR part 58.35, to be
submitted to EPA by each State on a
calendar quarterly basis, with
submissions due not later than 90 days
after the end of a quarterly reporting
period. Once air quality data have been
submitted to EPA, it is possible to ‘‘flag’’
specific values for various purposes.
‘‘Data flagging’’ refers to the act of
making a notation in a designated field
of an electronic data record. The
principal purpose of the data flagging
system in the AQS data base is to
identify those air quality measurements
for which special attention or handling
is warranted. These include, but are not
limited to, those measurements that are
influenced by exceptional events. In the
case of exceptional events, States place
the initial flag on the data in the AQS
data base. Following an evaluation of
the supporting documentation, EPA will
decide whether to concur with the flag;
concurrence will be marked by the
placement of a second flag in the AQS
data base by EPA. Once EPA has
concurred on the flag, the data will be
excluded from regulatory decisions such
as determinations of attainment or
nonattainment.
While the flagging of data by the State
is the first step in an exceptional events
demonstration, it is insufficient by itself
to allow for the exclusion of data. In
order to have EPA concur on a flag,
States must meet the additional
requirements described below. As
explained, the State has the
responsibility to document both the
occurrence of the event and the causal
connection to the monitoring data under
consideration. Because the initial step of
flagging the data is a relatively simple
one, States may flag many more days
than the number of days for which they
ultimately submit documentation to
support exclusion.
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B. What Does It Mean for an Event To
‘‘Affect Air Quality’’?
It is important to recognize that any
emissions-producing event has the
potential to have some influence on
downwind air quality. Indeed, on any
given day, measured air quality at any
given location will reflect the influences
of a variety of activities, including both
natural and anthropogenic emissions
from both local and remote upwind
sources. The EPA believes that it would
be unreasonable to exclude data affected
by an exceptional event simply because
of a trivial contribution of the event to
air quality. Furthermore, we also believe
that it would be unreasonable to
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exclude more significant, but routine
background air quality impacts, as this
would disregard an important part of
the public’s exposure to air pollution
upon which EPA’s air quality standards
are based. The effect of such exclusion
would be an inappropriate reduction in
the stringency of the NAAQS, rather
than providing specific relief under the
circumstances provided in section 319
for which States should not be
designated nonattainment or be required
to prepare control strategies.
Neither section 319 nor its legislative
history provides precise guidance on
what should be considered when
determining whether an event ‘‘affects
air quality’’ and thus qualifies to be
considered for exclusion or special
treatment. However, section
319(b)(3)(B)(ii) and (iv) provide that
there must be a ‘‘clear causal
relationship’’ between a measured
exceedance of a standard and the event
to show that the event ‘‘caused a
specific air pollution concentration;’’
and it must be shown that the data in
question are ‘‘directly due’’ to an
exceptional event. Moreover, one of the
principles provided by section
319(b)(3)(A) indicate that the protection
of public health is the highest priority.
For these reasons, we are proposing that
for an event to qualify as ‘‘exceptional’’
for purposes of special regulatory
consideration, its air quality impact
must fall both above the level of the
applicable standard (i.e., must be an
‘‘exceedance’’ as required by section
319) and significantly beyond the
normal fluctuating range of air quality,
including background air quality
concentrations, and should be large
enough so that without it there would
have been no exceedance. We next
provide several alternative approaches
to determining whether and when air
quality is ‘‘affected by’’ exceptional
events, and request comment on which
of these approaches is most suitable for
demonstrating such impacts.
1. Option 1: 95th Percentile Criterion
The first proposed approach is
essentially a test for statistical
deviations from the norm. For
measurement days on which the event
can be shown to have an air quality
impact, the measurement would be
compared to the 95th percentile of
measurements typical of days in the
particular calendar quarter that are not
influenced by exceptional events (‘‘nonevent days’’). The typical days could be
based on a 3–5 year period of record
which exclude days influenced by
exceptional events. Under this option,
only an event whose resulting
concentrations meet or exceed the 95th
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percentile criterion, along with meeting
the other criteria in this proposed rule
would qualify for exclusion from
regulatory consideration.
In evaluating available air quality
data, we have found that by limiting
consideration to those concentrations
above the 95th percentile, only those
concentrations that fall approximately
two standard deviations above the mean
of concentrations for that quarter would
generally be excluded (See memo from
Mark Schmidt, OAQPS, to docket
entitled ‘‘Analysis of Flagged Particulate
Matter Data,’’ February 10, 2006).
Excluding days on which
concentrations caused by exceptional
events exceed the 95th percentile
threshold employs a general test of
statistical significance and has the effect
of ensuring that such concentrations
would clearly fall beyond the range of
normal expectations for air quality
during a particular time of year.
In our analysis of flagged and
excluded air quality data for the period
1999–2004, we found that application of
the 95th percentile criterion would
result in the exclusion of approximately
85 percent of data previously flagged by
States and concurred on by EPA. Thus,
this approach would result in a
somewhat more rigorous qualification
requirement than is reflected in EPA’s
past case-by-case approach. Previously,
EPA did not have a concentration
threshold or other quantitative criteria
to determine which days would be
eligible for exclusion due to exceptional
events. As indicated above,
approximately 15 percent of the flags
that were concurred on were
concentrations that were not necessarily
statistically distinguishable from routine
levels. The 95th percentile approach
could also help to eliminate some of the
variability from State to State and
Region to Region: as described in
Schmidt (2006), rates of flagging and the
severity of pollution on flagged days
have varied significantly among States
and regions in the past. For PM2.5, for
example, many States flagged no days
between 1999–2004, while Puerto Rico
flagged 15 percent of all of its PM2.5
data. Also, while most PM2.5 flags
during this period were above the 95th
percentile, some States flagged data at
the 75th percentile or lower. (See memo
from Mark Schmidt, OAQPS, to docket
entitled ‘‘Analysis of Flagged Particulate
Matter Data,’’ February 10, 2006.)
2. Option 2: 75th Percentile/95th
Percentile Tiered Approach
Under this approach, we propose to
retain flexibility to determine whether
concentrations less than the 95th
percentile but above the norm should
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qualify for exclusion as ‘‘affecting air
quality.’’ In particular, multiple
measurement values over time with
relatively small individual event
impacts may collectively affect an
annual average concentration to a
significant degree. States may wish to
consider whether to exclude such
impacts if the average concentration is
close to the level of the annual NAAQS.
Therefore, we are soliciting comment on
a second approach whereby measured
values are compared both to the
historical 95th percentile of non-event
days and to the 75th percentile of such
days.
Where concentrations caused by an
exceptional event meet or exceed the
95th percentile criterion, they would be
conclusively determined to qualify for
exclusion subject to the other
requirements of this proposed rule.
Where concentrations caused by an
exceptional event do not meet the 95th
percentile criterion, we would provide a
further opportunity for States to make
demonstrations which satisfy the other
criteria in this proposed rule, so long as
values exceeded the 75th percentile of
non-event days. This approach would
provide for a more flexible approach
and would rely on a weight-of-evidence
demonstration that would permit States
to make other sorts of showings that the
concentrations caused by the event were
in some way unusual or not
representative of normal air quality and
thus should not result in additional
regulatory requirements.
When we applied the 75 percent
percentile criterion to our analysis of
flagged and excluded air quality data for
the period 1999–2004, we found that
this criterion would make nearly all of
the data previously flagged by States
and concurred on by EPA eligible for
exclusion. Thus, we expect this
approach would have a result that is
roughly consistent with EPA’s past caseby-case approach.
3. Option 3: Case-by-Case Approach
Based on Weight of Evidence
The third option is to permit the more
general case-by-case evaluation, without
threshold criteria, that may be guided by
the magnitude of the measured
concentration on days affected by
exceptional events relative to historical,
seasonally adjusted air quality levels.
This approach is most nearly analogous
to our historical treatment of
exceptional events but, in contrast to
Options 1 and 2, provides the least
definitive guidance to assist States in
their evaluations. Nevertheless, the
case-by-case approach allows for
consideration of days with ambient
concentrations which are not
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necessarily among the highest
concentrations that have been
historically observed. In fact, 25 percent
of days have concentrations greater than
the median value but less than the 75th
percentile. While such days are unlikely
to impact short-term standards,
discounting such days can certainly
have an impact on an annual average
concentration. In general, however,
demonstration that an event caused a
concentration which is essentially
indistinguishable from routine air
quality would be very difficult to
document, and this approach may make
it difficult for EPA regions to be
consistent when determining whether to
concur on a flag.
We request comment on which of
these proposed options should be
included in the final rule, including the
appropriateness of proposed statistical
criteria, the period of record on which
to base the 95th and 75th percentile and
conclusions about normal air quality
expectations (e.g., 3 years, 5 years, or
some longer period of record), and any
other criteria or procedures we should
consider adopting along with one of
these options.
C. Use of a ‘‘But For’’ Test
There may be instances in which
exceptional events may have a
significant impact on air quality on days
when concentrations are already above
the applicable standard in the absence
of the influence of such events. In such
cases, it is important to preserve and
consider all valid air quality data
influenced by activities which properly
fall within the responsibilities of States
to manage for purposes of air quality
attainment and maintenance. For this
reason, we are proposing to require that
air quality data may not be excluded
except where States show that
exceedances or violations of applicable
standards would not have occurred ‘‘but
for’’ the influence of exceptional events.
In other words, to the extent it is
possible to determine that the resulting
air quality concentrations and
appropriate design values for an area
would be above the level of the
standards even without the influence of
the exceptional event, the air quality
data for the day(s) in question should
not be excluded. However,
consideration of the impacts of
exceptional events on air quality values
for control strategy planning purposes
may be appropriate, and States are
encouraged to consult with the
appropriate EPA regional offices to
further discuss this issue.
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D. Schedules and Procedures for
Flagging and Requesting Exclusion of
Data
In establishing procedures and
timetables for States to request, and EPA
to grant, exclusion of data affected by
exceptional events, we are guided by
two competing considerations: ensuring
States have adequate time and
opportunity to compile and evaluate all
relevant and available information in
support of such requests; and making
determinations in a timely manner so
that all pertinent and valid air quality
data would be appropriately considered
in regulatory determinations. To assist
EPA in determining the best approach to
managing the data flagging process and
submissions of demonstrations for the
final rule, we are proposing three
alternatives for public review and
comment.
1. Option 1: Early Data Flagging and
Demonstration Submission
The first approach would establish a
two-step process for identification of
data and submission of demonstrations.
This process provides for the early
flagging of data and the notification of
the appropriate EPA Regional Office
concerning the State’s intention to seek
exclusion of data, followed by a longer
timeframe for States to prepare and
submit their demonstrations.
Under this approach, we would
require a State to flag the data that they
believe to be affected by exceptional
events at the time of submission of the
air quality data to EPA’s AQS data base,
in accordance with the schedule
described in 40 CFR part 50.35, which
is generally no later than 90 days after
the end of the calendar quarter. This
approach would ensure that the flagging
process remains consistent with the
timeline set forth in rules governing
data submission requirements.
Just as the scope and substance of
demonstrations in support of requests
for exclusion will vary depending on
facts and circumstances (see section
IV.F. below), so, too, will the time
required for such demonstrations.
Where air quality in an area is
influenced by a relatively small set of
emission sources with well-defined
emission profiles and limited pollutant
species, a demonstration that an air
quality measurement influenced by a
particular event merits exclusion may
be relatively simple to make. In other
cases, such as where the number and
types of sources contributing to
measured air quality concentrations are
extremely complex and varied, making
it more difficult to distinguish between
the effects of routine activities and
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unusual ones, more time and effort will
be needed for a State to provide an
adequate demonstration in support of its
request.
For these reasons, we are proposing
under this option to require States to
notify the appropriate EPA Regional
Office of their intent to seek exclusion
of data due to exceptional events at the
time of submission of quarterly air
quality data to the AQS data base. We
are also proposing to require the State
to consult with the EPA Regional Office
as soon as reasonably possible after
notification about the event, its
suspected air quality impact, and the
demonstration needed to justify a
decision to exclude the data from
regulatory consideration. This is
intended to enable the State and EPA to
work together during the process of data
analysis and documentation to ensure
that a complete and well-supported
demonstration is submitted in a timely
manner.
With respect to demonstrations in
support of requests for exclusion of
data, we are proposing under this option
to provide States with more time to
submit the necessary demonstration. We
propose that States submit complete
demonstrations to EPA not later than
180 days following the close of the
quarter in which the event occurred.
Based on past experience with
exceptional events and associated data
analyses, we believe that this will
provide adequate time in most cases for
States to identify, compile, and evaluate
all relevant factors pertaining to an
exceptional event and its impacts.
However, in special circumstances
where additional time is required to
make a complete submission, and where
the outcome of such additional efforts is
likely to have a substantial impact on
the demonstration, we are proposing to
allow States to request extensions of up
to 90 additional days. We expect that
such extensions under this option
would be the exception, rather than the
rule, and that they will be limited to
special circumstances necessitating
more complex and sophisticated
analyses, such as where the collection
and analysis of species-specific data in
urban areas may be needed in order to
characterize and quantify an event’s
contribution to air quality at a particular
location. Under this option, as well as
the options addressed below, once EPA
receives a State’s demonstration, EPA
will then have a 30-day period to review
the demonstration and provide a
concurrence or nonconcurrence on the
flag in the AQS data base. The EPA
expects that, in most cases, a period of
30 days will be enough time to review
and provide a concurrence related to a
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State’s request to exclude data affected
by an exceptional event. However, for
more complex demonstrations, EPA
may require more time for its review. In
such cases, EPA may extend the time for
its review by not more than an
additional 30 days.
2. Option 2: Early Data Flagging and
Delayed Demonstration Submission
Under this option, we are proposing
the same requirements for the flagging
of data and notification of the
appropriate EPA Regional Office as
described in Option 1. However, under
Option 2, we propose to allow up to 3
years following the quarter in which the
event occurred for the submission of
exceptional events demonstrations. The
reason for providing more time under
this option is that for most existing air
quality standards, decisions regarding
whether or not an area is attaining the
applicable standard are based on the
most recent 3 years of air quality data.
Providing 3 years for submission of
demonstrations would provide States
with an opportunity to evaluate whether
the influence of one or more exceptional
events will be relevant to
determinations of attainment or
nonattainment before undertaking the
effort of preparing and submitting
demonstrations.
3. Option 3: Delayed Data Flagging and
Demonstration Submission
Under this option, we are proposing
to decouple the process of flagging and
demonstrations from the regular
submission of air quality data to the
AQS data base and to require instead
that data be flagged and exceptional
events demonstrations be submitted not
later than 6 months prior to the date
when regulatory decisions using the air
quality data must be made. This option
is based on the recognition that while
data flagging itself may not be a
particularly burdensome exercise, it
triggers a more extensive process of
collection and analysis of other
information to determine and
demonstrate whether, in fact, an
exceptional event has occurred which
affects air quality data in a way that
justifies exclusion of the data. It may be
that although certain events occurred
which do indeed affect air quality in
significant ways, their impact on
regulatory decisions may not be known
for a significant period of time, i.e., until
a relevant 3-year period of record is
compiled and the need for a regulatory
decision is identified. Thus under this
option, it would be less burdensome for
the States and EPA if demonstrations
were not required unless and until it
became apparent that potentially
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affected measurements would be used
in making regulatory findings of
attainment or nonattainment (e.g.,
where a State with an existing area
designated as nonattainment seeks to
have that area redesignated as
attainment and the existence of one or
more exceptional events may affect its
ability to provide the requisite 3 years
of clean air quality data).
We request comment on which of the
above three proposed options EPA
should promulgate and on what, if any,
modifications to these options we
should make prior to the final rule.
E. Exclusion of Entire 24-Hour Value as
Opposed to a Partial Adjustment of the
24-Hour Value
The EPA’s historical practice has been
to exclude a daily measured value in its
entirety when that value is found to be
largely caused by an exceptional event,
and we are proposing to retain this
approach in today’s proposed rule. With
this approach, a determination is made
that emissions from the event are largely
responsible for the resultant ambient air
pollutant concentration. For example, if
the observed concentration is 200 µg/m3
PM2.5 and is associated with a nearby
forest fire, then EPA would concur with
the claim that the event was responsible
for the ambient concentration. The
measured value would be excluded in
its entirety from the data used to judge
attainment (as per 40 CFR 50, appendix
N), although the measurement day
would still count towards meeting
minimum data capture requirements.
We believe it would be desirable to
adjust the daily value to exclude only
those portions of the data that are
attributable to the exceptional event in
question, and to retain the remainder of
the day’s measurement if appropriate
and accurate methods were available to
make such adjustments. For example, if
an area affected by a forest fire had a
measured 24-hour PM2.5 concentration
of 50 µg/m3 and the estimated event
impact was 30 µg/m3, then the expected
value which would have occurred but
for the event would have been 20 µg/m3.
Normal air quality for this location
might be 16 µg/m3 and, therefore, the
‘‘but-for’’ concentration of 20 µg/m3 is
above average. Discounting the entire
event day could, therefore,
inappropriately bias a determination of
nonattainment with the annual PM2.5
NAAQS (currently set at 15 µg/m3). We
are currently seeking to develop and
evaluate new analytical methods that
would allow us to discount only the
portion of the daily value attributable to
the exceptional event. However, at
present, we are not aware of the
existence of adequate and universally
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applicable techniques that are
administratively and technically
feasible and that could support partial
adjustment of air quality data except
perhaps in limited cases, such as where
the number and type of pollutant
species and contributing sources are
relatively less complex or potentially,
when sufficient spatial, temporal,
meteorological and chemical data are
available [See memo to docket, Husar et
al. 2006, (https://www.regulations.gov,
Epa–HQ–Oar–2003–0061–0733 thru
0733.5)]. When we determine that
techniques for adjustment of air quality
data are sufficiently well-demonstrated
for use in exceptional events
determinations, we will publish a notice
of proposed rulemaking to seek
comment on the appropriateness and
scope of such use.
F. What Should States Be Required To
Submit in Their Exceptional Events
Demonstrations?
Section 319 requires that, in order to
have a flagged value excluded from
regulatory determinations, a State must
make an affirmative demonstration that
an event occurred (as shown by reliable
and accurate data that is promptly
produced) and that there is a clear
causal relationship between measured
exceedances or violations of a standard
and the exceptional event in question to
‘‘demonstrate that the exceptional event
caused a specific air pollution
concentration.’’ (42 U.S.C.
7619(b)(3)(B)(ii), (iv)). Section 319 also
indicates that regulations promulgated
under the section should provide for
criteria and procedures to exclude air
quality monitoring data ‘‘directly due to
exceptional events from use in
determinations by the Administrator
with respect to exceedances or
violations of the national ambient air
quality standards.’’
Therefore, after flagging data in the
AQS data base, States are expected to
develop appropriate documentation to
support each individual flag. As a
general matter, we believe that such
demonstrations should include
documentation showing that the event
in fact occurred and that emissions
related to the event were transported in
the direction of the monitor(s) where
measurements were recorded; the size of
the area affected by the transported
emissions; the relationship in time
between the event, transport of
emissions, and recorded concentrations;
and, as appropriate, pollutant speciesspecific information supporting a causal
relationship between the event and the
measured concentration. The latter
information could be based on available
data provided by routine speciation,
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monitoring networks, or from selective
laboratory analysis of archived
particulate matter filters for the day
thought to be impacted by specific
events. In certain situations, such data
might be useful for evaluation of
impacts from exceptional events, e.g., to
distinguish between impacts caused by
natural fires versus impacts caused by
industrial sources. Depending on which
option is finalized pursuant to section V
below, States may also need to show
that appropriate mitigation actions were
taken at the time that the event
occurred, or after an event occurred in
order to protect public health.
The following examples are intended
to further illustrate the kinds of
information that States could consider
in preparing their demonstrations:
1. Information demonstrating the
occurrence of the event and its
subsequent transport to the affected
monitors. This could include, for
instance, documentation from land
owners/managers, satellite-derived
pixels (portions of digital images)
indicating the presence of fires; satellite
images of the dispersing smoke and
smoke plume transport or trajectory
calculations (calculations to determine
the direction of transport of pollutant
emissions from their point of origin)
connecting fires with the receptors.
2. Identification of the spatial pattern
of the affected area (the size, shape, and
area of geographic coverage). This could
include, for instance, the use of satellite
or surface measurement data.
3. Information about temporal
patterns (e.g., the time and duration of
an event in relation to measured
downwind concentrations, air quality
trends over time and space). This could
include, for instance, observed
sequential concentration spikes at
multiple locations in a downwind
direction.
4. Identification of the chemical
composition of measured
concentrations. This could include, for
instance, organic or crustal material in
excess of typically observed quantities
to differentiate from other high
concentration events.
5. Extremely high wind speeds, or
unusual transport conditions relative to
historically typical levels for the season
of the year in which the claimed event
occurred.
This list is not exhaustive and not all
of these kinds of information and/or
documentation will need to be provided
in every instance. A particular instance
may require more or less
documentation, depending on the
particular facts or circumstances in that
instance. The simplest demonstrations
could consist of newspaper accounts or
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satellite images to demonstrate that an
event occurred together with daily and
seasonal average ambient concentrations
to demonstrate an unusually high
ambient concentration level which is
clearly indicative of an exceptional
impact. Such is the case with events
such as volcanic eruptions and nearby
forest fires. In one instance, we
determined that wildfires upwind of the
San Diego area caused high
concentrations of particulate matter
measured in October 2003 based on the
actual physical damage caused by fire to
the ambient monitor. Depending on the
nature of the event, meteorological
conditions, severity and spatial extent of
measured ambient concentrations
(including relevant chemical
components when available) relative to
what typically occurs in the area, and
on emissions of pollutants from the
exceptional event which have similar
characteristics to those of other sources
in the area, additional showings could
be required on a case-by-case basis. In
particular, we anticipate that
significantly more effort will be needed
to establish that an exceptional event
caused a particular concentration in an
urban area in which there are numerous
and diverse sources and complex
meteorology and topography, and where
the emissions from the event in question
may well be similar to those from other
sources contributing to measured
concentrations, as compared to an area
that has relatively few sources, simple
terrain and less complex meteorology,
and where emissions associated with
the event are both substantially greater
than and different in composition from
those of other nearby sources. Because
of the variability in the nature of
exceptional events and the resulting
demonstration requirements, States
should consult with the appropriate
EPA Regional Office early in the process
of preparing their demonstrations.
We are not proposing to specify what
will be required as a minimum level of
documentation in all cases because facts
and circumstances will vary
significantly based on, among other
things, geography, meteorology and the
relative complexity of source
contributions to measured
concentrations in any particular
location. However, we request comment
on whether we should adopt a set of
minimum demonstration requirements
to ensure a reasonable degree of national
consistency in approaches to
demonstrating exceptional events, and if
so, what elements should be included in
the demonstration. We believe,
however, that at a minimum, the
elements of such a demonstration
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should include a showing that an event
occurred at a time when meteorological
conditions were conducive to
transporting emissions from the event
downwind to the monitor recording a
high concentration of one or more
criteria pollutants.
G. Special Considerations Relevant to
Proposed Standards for PM10–2.5
As noted in EPA’s notice of proposed
rulemaking reviewing the NAAQS for
particulate matter (71 FR 2620; January
17, 2006), fine particles (PM2.5) are
produced chiefly by combustion
processes and by atmospheric reactions
of various gaseous pollutants, whereas
thoracic coarse particles (PM10–2.5) are
generally emitted directly as particles as
a result of mechanical processes that
crush or grind larger particles or the
resuspension of dusts. Sources of fine
particles include, for example, motor
vehicles, power generation, combustion
sources at industrial facilities, and
residential fuel burning. Sources of
thoracic coarse particles include, for
example, resuspension of traffic-related
emissions such as tire and brake lining
materials, and direct emissions from
industrial operations, construction and
demolition activities. Fine particles can
remain suspended in the atmosphere for
days to weeks and can be transported
thousands of kilometers, whereas
thoracic coarse particles generally
deposit rapidly on the ground or other
surfaces and are not readily transported
across urban or broader areas (71 FR
2620, 2625; January 17, 2006).
Based on preliminary analysis, we
generally anticipate that demonstrations
that ambient concentrations of PM10–2.5
have been affected by exceptional
events will involve similar analytical
steps to demonstrations for PM2.5 but
will be simpler than demonstrations for
PM2.5.9 This conclusion is based on
preliminary evaluation of estimated
PM10–2.5 concentrations derived from
historical PM10 and PM2.5 data. We
examined those days on which PM10
exceedances were flagged as due to
exceptional events but where PM2.5
concentrations were not also flagged,
indicating that the event in question
was dominated by coarse particles. The
results of this analysis suggest that
exceptional events related to PM10–2.5
are relatively infrequent, occur
predominantly in the western States and
are overwhelmingly high wind events.
Thus, with the exception of western
areas, we do not anticipate that
exceptional events will be a
9 The demonstrations related to PM
10–2.5 are
contingent upon the final outcome related to the
rulemaking on the NAAQS for PM10–2.5.
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predominate factor in decisions made
related to attainment or nonattainment
determinations for the proposed
PM10–2.5 standards (See memo from
Mark Schmidt, OAQPS, to docket
entitled ‘‘Analysis of Flagged Particulate
Matter Data,’’ February 10, 2006).
Moreover, in light of the above analysis
and the evidence on which it is based,
we believe that exceptional events
demonstrations for PM10–2.5 will involve
relatively straightforward showings that
when high concentrations occurred at
the affected monitors, concentrations at
available rural monitors (e.g., IMPROVE
network monitors) were also elevated
and that meteorological conditions (i.e.,
wind speed and wind direction) were
conducive to transport from upwind
sources of re-entrained coarse particles.
It may be beneficial to examine
continuous PM10–2.5 monitoring data as
well, as they may indicate extremely
high short-term values (e.g., 1 hour or
less) that heavily influence 24-hour
concentrations and are consistent with
extreme high wind events. For instance,
when we examined air quality
concentrations recorded in El Paso,
Texas during a dust storm that occurred
on April 26–27, 2002 we found two
consecutive 24-hour average
concentrations of PM10 (654 µg/m3) and
PM2.5 (56 µg/m3) which were dominated
by a peak 1-hour concentration of 2700
µg/m3 which occurred in the late
evening of April 26–27.
H. Public Availability of Air Quality
Data and Demonstrations Related to
Exceptional Events
Sections 40 CFR parts 58.35 and 58.28
of EPA’s air quality monitoring rules
state that all data, flagged or unflagged,
should be available to the public for
comparison to the NAAQS to determine
if exceedances have occurred. The EPA
is proposing to require that all relevant
flagged data, along with the reasons for
the data being flagged, and a
demonstration that the flagged data are
caused by exceptional events be made
available by the State for public review
and comment prior to the demonstration
being submitted to EPA for a decision
concerning whether to exclude the data
from regulatory consideration. Notice
and availability of such data and
demonstrations must be adequate and
consistent with States’ administrative
procedures governing similar
submissions. EPA is not proposing to
require that public hearings be held on
exceptional events demonstrations, but
leaves this matter to the States’
discretion.
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V. Additional Requirements
Pursuant to section 319, EPA is
proposing new regulations to address
exceptional events. Also EPA is
proposing one option, and is taking
comments on three alternative options,
to address the issue of whether, and to
what extent, States might be required to
adopt specific mitigation plans or
measures. Section 319 states that EPA
must promulgate regulations that are
consistent with paragraph 3 which
enumerates certain principles and
minimum regulatory requirements. The
first part of paragraph 3 states that in
promulgating regulations under section
319, EPA shall follow five principles,
including the principle that each State
‘‘must take necessary measures to
safeguard public health regardless of the
source of air pollution.’’ Section
319(b)(3)(A). This section does not,
however, specify what measures may be
‘‘necessary’’ in this context. In order to
address this principle, EPA is proposing
to exclude trivial and more routine
background air quality impacts from
qualifying as an exceptional event and
is also proposing a ‘‘but for’’ test as a
precondition to qualification as an
exceptional event (See: section IV). In
addition, EPA is also proposing one
approach and is taking comments on
three other alternative options
concerning State actions in anticipation
of or in response to exceptional events.
These proposed options range from
being very detailed and more
prescriptive to very flexible and less
prescriptive. While EPA does not
believe section 319(b)(3)(A) explicitly
requires, in and of itself, that States
develop mitigating measures or plans
under options (1), (2), and (3) as
discussed below, EPA solicits comment
on whether this subparagraph supports
the exertion of other legal authority to
require mitigating actions or plans and
solicits comment on issues regarding its
legal authority to require mitigation
measures and plans, and the legal basis
for not requiring mitigation measures or
plans. We are also requesting comments
on the proposed approach and the three
alternatives, and on any modifications
to or combinations of any of the four
approaches.
A. Option 1: Proposed Option: Require
Public Notification, Education and
Appropriate and Reasonable Measures
In cases where exceedances or
violations of a NAAQS are caused by an
exceptional event, EPA is proposing that
once a State becomes aware that an
exceptional event is occurring, is
predicted to occur, or has occurred, the
State must take appropriate action to:
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1. Provide notice to the public of the
event. This may include, but is not
limited to, using the media to alert the
public of the event.
2. Provide public education
concerning the potential health risks
associated with being exposed to high
ambient concentrations of pollutant(s)
related to the event. This may include,
but is not limited to, providing
information to sensitive populations
related to the health risks associated
with the event.
3. Take appropriate and reasonable
measures to abate or minimize the
exposure of the public to high
concentrations of air pollution
associated with the exceptional event.
This may include, but is not limited to,
taking reasonable and appropriate
actions to implement control measures
on significant contributing
anthropogenic sources to reduce
potential exposure of the public to
emissions associated with natural
events. For example, in the case of
volcanic or seismic activity, this may
include, but is not limited to, providing
for prompt clean up of the ash deposits
related to the event to prevent reentrainment.
Under this option, where a State is
requesting that air quality data be
excluded as an exceptional event, the
State must submit, as part of its
demonstration, the appropriate
documentation to show that the State
provided appropriate public notice and
public education concerning the event
in question, and that the State took
reasonable measures to abate or
minimize the exposure of the public,
where appropriate.
The concept of having States take
steps to reduce emissions, where
appropriate, and to develop mitigation
plans to address impacts associated
with exceptional events was first
instituted under the PM10 Natural
Events Policy. The mitigation plans
required under the PM10 Natural Events
Policy were called Natural Events
Action Plans (NEAPS). In instances
where a State requested that air quality
data influenced by a natural event be
excluded, the State was required to
develop and implement a NEAP.
In developing a NEAP, States were
expected to: Establish a public
notification and education program
related to natural events; minimize
public exposure to high concentrations
of pollutants related to natural events;
provide a process for abatement of
controllable anthropogenic sources
related to natural events; identify, study,
and implement practical mitigation
measures as necessary; and provide for
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a periodic re-evaluation of the NEAP
every 3–5 years.
Due to past success with the
implementation of NEAPs, EPA is
proposing to base the requirements to
mitigate the impact of exceptional
events on the general concepts and
elements described above from the PM10
Natural Events Policy. The EPA is
proposing this approach to provide
flexibility to the States to implement
those measures that it considers to be
reasonable and appropriate under
particular circumstances to protect
public health in the event of an
exceptional event. The EPA believes
that this approach allows States to use
their experience in addressing those
exceptional events that occur most
frequently in their respective
jurisdictions, and in providing notice to
sensitive populations concerning the
harmful effects of prolonged exposure to
high concentrations of pollution
associated with various types of
exceptional events, yet could be
consistent with both the principles and
requirements of section 319. The
proposed approach also allows EPA to
fulfill its oversight responsibility, while
still providing flexibility to States to
implement reasonable measures to
address the effects of exceptional events
on public health. A possible
disadvantage of this option is that it has
the potential to result in inconsistencies
in the way that exceptional events are
addressed by States and in the actions
that are taken to mitigate public health
impacts associated with exceptional
events, although such inconsistencies
exist in any program that allows
flexibility of any kind. We believe that
despite this, such flexibility makes for a
better and more efficient program in
terms of taking specific mitigation
actions that fit the circumstances of
each case.
B. Option 2: The Development of a
Mitigation Plan by States Under Section
110 of the CAA
Under this option, States would be
required to adopt a general mitigation
plan to address exceptional events
before the occurrence of an event as a
part of the State’s SIP required under
section 110(a)(1) of the CAA. Section
110(a)(1) requires States to adopt and
submit to EPA, within 3 years following
the promulgation of a new or revised
NAAQS, a plan which provides for the
implementation, maintenance, and
enforcement of the standard in each air
quality region within the State. The EPA
believes that section 110(a)(1) of the
CAA provides EPA with the statutory
authority to require States to submit
plans to address the mitigation of public
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health impacts due to exceptional
events that cause exceedances or
violations of the NAAQS, because such
plans assist in the maintenance and
enforcement of the NAAQS and could
be consistent with both the principles
and requirements of section 319. Under
this alternative, States would be
required to develop and adopt the
general requirements and procedures
necessary for the implementation of a
mitigation plan as a part of its section
110(a)(1) SIP to address a new or revised
NAAQS. As a part of this plan, EPA
would require States to identify the
actions the State intends to take to
reduce the impact of exceptional events
on public health. Since the precise
nature and cause of exceptional events
may not be foreseeable, in many cases,
these requirements would be general,
and similar to the types of actions that
States have already identified and
adopted in their section 110 plans
intended to address emergency episodes
as required under section 110(g) and 40
CFR part 51.152. Once the general
requirements of the mitigation plan are
in place under section 110, the State
would only need to take action on an
episodic basis to implement the
requirements of the mitigation plan for
the affected area following the
occurrence of an exceptional event.
The general plan requirements would
include provisions for providing public
notification of an event; providing a
program to educate the public on the
harmful effects of prolonged exposure to
emissions associated with an
exceptional event; and implementing
reasonable measures to mitigate the
public health impacts of an exceptional
event (e.g., the implementation of
control measures to abate or minimize
the effect of high concentrations of
emissions associated with an
exceptional event). In cases where
control measures are required to address
the impacts associated with an
exceptional event, the State would
implement the required measures on an
episodic basis, meaning in response to
a specific event that affects the air
quality of a particular area.
In cases where anthropogenic sources
contribute to emissions related to a
recurring natural event, appropriate
control measures would have to be
implemented on all significant
contributing anthropogenic sources
related to the event in the affected
area.10 Natural events, which are
10 In the case of the proposed NAAQS for
PM10–2.5, these options would not apply to sources
which are proposed to be excluded from
consideration, e.g., agriculture and mining
activities.
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defined as a class of exceptional events
under this rule, may recur frequently in
affected areas. Under this option, as
well as under Option 3 below, after a
natural event occurs, and it is
determined that anthropogenic sources
have significantly contributed to the
emissions associated with that event,
EPA is proposing that at a minimum,
Reasonably Available Control Measures
(RACM) must be implemented on the
anthropogenic sources that contributed
to the emissions associated with the
event. Reasonable Available Control
Measures are defined as those control
measures that are considered to be
reasonable, and economically feasible,
to implement in an area for a given
source type. States should consult the
most recent EPA control guidance for
the affected pollutant to determine what
control measures might be considered as
RACM for the affected source types
associated with emissions due to a
natural event. This requirement is also
consistent with the policy currently
being implemented under the ‘‘PM10
Natural Events Policy.’’
Also, EPA requests comments on
whether, instead of RACM, the
appropriate level of controls that should
be implemented on these source types is
Best Available Control Measures
(BACM). Best Available Control
Measures is a term first identified in the
CAA under part D, subpart 4, related to
the implementation of the PM10
standard. For PM10, BACM are defined
as techniques that achieve the
maximum degree of emissions
reductions from a source as determined
on a case-by-case basis, considering
both the technological and economic
feasibility of implementing the control
measures for the affected source (59 FR
42010; August 16, 1994). Currently, EPA
requires the implementation of BACM
on contributing anthropogenic sources
under the PM10 Natural Events Policy
for high wind events. Under this option,
as well as under Option 3 below, the
State would also be required to submit
the mitigation plan for the affected area
to the appropriate EPA Regional Office
for review and concurrence. Once the
State has received concurrence from the
Regional Office on the control measures
identified for the anthropogenic sources
contributing to exceedances associated
with natural events, the State would be
required to include the measures as a
part of its section 110(a)(1) SIP related
to the mitigation plan for the area. As is
the case with the control plans required
for emergency episode plans under
section 110(g), the State will not be
required to submit the specific control
measures as a part of the mitigation plan
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to EPA to be made federally enforceable.
Pursuant to section 107(d)(3)and section
319 (b)(3)(B) of the CAA, it is EPA’s
intention to adopt a flexible approach
and not redesignate an area as
nonattainment, or seek a SIP call for an
area, so long as the State continues to
implement the requirements related to
the mitigation plan for the area, as well
as the control measures for significant
contributing anthropogenic sources
related to a natural event.
Where a State provides adequate
documentation to show that RACM was
being implemented for the affected
sources at the time that the natural
event in question occurred, a State need
not implement further control measures
in the area related to the natural event.
In cases where RACM was not
implemented for contributing
anthropogenic sources at the time of the
natural event, the State would be
required to implement RACM as
expeditiously as practicable, but in no
case later than 18 months from the end
of the calendar quarter in which the
event occurred. The EPA requests
comments on whether this proposed
time period is appropriate for the
implementation of RACM for significant
contributing anthropogenic sources
under this option or whether another
time period is more appropriate.
The advantage of this particular
option is that all States would have a
general plan in place for how to address
exceptional events once they occur and
could take immediate action to protect
public health. It would also allow States
to evaluate proactively what actions
need to be taken to address
anthropogenic sources related to
exceptional events, and to consider the
most efficient and effective ways to
educate the sensitive populations most
likely to be harmed should an event
occur.
It is important to note that if we
selected Option 3 regarding the timeline
for flagging of data and submission of
demonstrations, a disadvantage would
be that flagging and demonstrations
could potentially be delayed
significantly past the time when States
would be required to implement RACM
under this option for mitigation plans.
We request comment on when RACM
should be implemented by States in the
event that we select Flagging and
Demonstration Option 3.
C. Option 3: The Development of a
Mitigation Plan for Episodic Events
Under this option, where appropriate,
EPA would require a State to develop
and implement a mitigation plan for an
area following the occurrence of an
exceptional event. This is in contrast to
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Option 2 above, which would require
each State to adopt a plan under section
110 of the CAA containing the general
provisions of a mitigation plan in
advance of the occurrence of any
exceptional event. Under this third
option, the mitigation plan would only
be developed by the State following the
occurrence of an exceptional event for
which a State requested exclusion of air
quality data. The mitigation plan would
be required to address the actions that
would be taken by the State related to
future similar events, yet could be
consistent with the principles and
requirements of section 319. The
mitigation plan under this option would
have the same provisions to plans
developed under Option 2 above,
including the requirements to notify the
public that an event is expected to
occur, or is occurring, or has occurred,
to provide for public education related
to the health effects associated with the
event, and to identify the actions that
would be taken by the State to mitigate
the impact of any recurrence of the
event on public health. The mitigation
plan must include a detailed description
of planned actions that would be
implemented if the event recurs. It
would also provide for an
implementation schedule which
identifies the actions that would be
taken related to the recurrence of an
event, and it should identify the
principal parties that would be
responsible for carrying out the stated
actions under the mitigation plan.
In cases where a State intends to
request that EPA exclude data from
regulatory consideration that has been
affected by an exceptional event under
this option, the State must submit the
plan to EPA for review and concurrence.
However, EPA will not take action to
make the mitigation plan federally
enforceable. Under this option States
would develop a mitigation plan for an
area where an exceptional event has
caused an exceedance or violation of a
NAAQS no later than 18 months
following the end of the calendar
quarter in which the event occurred.
The EPA requests comments on whether
18 months is an appropriate time period
for the development and adoption of a
mitigation plan under this option or
whether another time period is more
appropriate.
As stated in Option 2 above, in cases
where anthropogenic sources contribute
to emissions related to a recurring
natural event, RACM must be
implemented for all significant
contributing anthropogenic sources.
Where a State provides adequate
documentation to show that RACM was
being implemented for the affected
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sources in the area at the time that the
event occurred, no action would be
required by the State to implement
further control measures related to the
event for the affected area. In cases
where a determination is made that
RACM was not being implemented for
significant contributing anthropogenic
sources at the time of the event, the
State would be required to adopt and
implement RACM as expeditiously as
practicable, but in no case later than 3
years following the end of the calendar
quarter in which the event occurred.
The EPA requests comment on the
appropriateness of the time period being
proposed for the implementation of
control measures related to significant
contributing anthropogenic sources
associated with a recurring natural
event under this option.
An advantage of this alternative is
that a State can more carefully tailor the
actions that it will take to mitigate the
effect of the exceptional event based on
its prior experience, which will help
ensure protection of public health.
However, the disadvantage of this
particular option is that it would apply
more specifically to one type of event,
so that if a new or different type of
exceptional event occurred, there would
be no provisions in place under the
mitigation plan to address it. Each time
a new type of event occurs, the State
would need to submit or revise the plan
to address the new event.
D. Option 4: Do Not Require States To
Adopt and Implement Specific
Mitigation Plans or Measures Under
This Rule
Under this option, EPA would not
require a State to develop and
implement a mitigation plan for
exceptional events, or to take specific
mitigation measures as described in
options 1–3 in order for EPA to exclude
data from regulatory consideration
because it results from an exceptional
event. This approach would allow
States to have the maximum degree of
flexibility in determining what actions
should be taken to mitigate the impacts
of exceptional events, e.g., public
notification, public education, efforts to
reduce exposures, or other necessary
measures to safeguard public health.
Thus, States would not be obligated to
take any particular actions to mitigate
exposures such as those in Option 1, to
develop and implement a formal
mitigation plan as part of the SIP such
as that in proposed Option 2, or to
develop a more formal plan with
requirements not a part of the SIP such
as that in proposed Option 3.
This proposed approach would
require a much less formal method for
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States to take necessary measures to
safeguard public health, yet could be
consistent with both the principles and
requirements of section 319. The statute
does not identify specific ways in which
EPA must satisfy its principles and
requirements. Moreover, as detailed
above, EPA is proposing to exclude only
certain types of exceptional events from
regulatory determinations with respect
to the NAAQS. In section IV, EPA is
proposing options for percentile criteria,
case-by-case evaluation, and
establishment of a ‘‘but for’’ test in order
for an event to qualify as an exceptional
event for which data can be excluded
with respect to exceedences or
violations of the NAAQS. These
requirements, in and of themselves, may
offer appropriate protection of public
health. Under this view, EPA should
give States broad flexibility in
determining how best to respond to
individual exceptional events. Given the
States’ concern with the health of their
citizens, and taking into consideration
the other requirements of this rule, in
this view States would have sufficient
incentive to take appropriate actions to
protect public health.
One benefit of this option is that it
would allow States to maintain the
maximum degree of flexibility to
respond to exceptional events and to
take appropriate actions to protect
public health without unnecessarily
limiting their ability to seek exceptional
events treatment for the data. One
potential limitation of this proposed
approach is that it might result in
inconsistencies among States in
addressing exceptional events and in
mitigating the impacts of those events.
The EPA requests comments on all
options described above. Additionally,
EPA requests comments on specific
modifications that should be made to
one or more of the options provided
above, or on any combination of these
options.
VI. Special Treatment of Certain Events
Under This Rule
As stated in section III.C., above, this
proposed rule applies to data affected by
natural events, which are a subset of
exceptional events, at air quality
monitoring sites where it has been
determined that concentrations due to
these events have caused or
substantially contributed to exceedances
or violations of the NAAQS in an
affected area. This proposed rule applies
to several types of natural events,
including volcanic and seismic actives,
natural disasters, high wind events,
unwanted fires, and stratospheric ozone
intrusions, and to transported pollution
originating from national and
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international sources that otherwise
meets the criteria and requirements for
exceptional events. Some types of
exceptional events have unusual
characteristics which require special
consideration in the context of this
proposed rulemaking. We discuss each
of these special issues, and the
necessary accommodations, below.
A. Volcanic and Seismic Activities
Volcanic and seismic activities may
affect air quality for an extended period
of time after the initial occurrence of the
event in question. Therefore, EPA
believes it is appropriate to consider an
extended timeframe for flagging and
exclusion of data associated with such
events. Specifically, EPA is proposing
that emissions attributed to
anthropogenic activities that re-entrain
volcanic ash and dust from seismic
activity during the first year (12 months)
following an event will be treated as due
to the natural event. Based on prior
experiences, and on consultation with
States, we believe that 1 year is an
adequate amount of time for cleaning
ash deposits from areas where
anthropogenic activities (e.g., vehicle
traffic) may cause re-entrainment and
possible exceedances of the particulate
matter NAAQS. After a year, however,
exceedances or violations due to reentrainment of ash deposits will not be
provided special consideration under
this rule. The EPA, however, requests
comments on whether another time
period is more appropriate and
reasonable to allow for clean up of ash
deposits following volcanic or seismic
activity.
B. High Wind Events
Where high wind events result in
exceedances or violations of PM2.5
standards, we are proposing that they
will be treated as natural events
pursuant to this proposed rule if there
is a clear causal relationship
demonstrated between the exceedances
measured and the high wind event in
question, and if anthropogenic activities
which contribute to PM2.5 emissions in
conjunction with the high wind event
are reasonably well controlled.
For the proposed 24-hour PM10–2.5
standard, we propose to exclude
measured exceedances from
consideration if it is demonstrated that
high winds resulted in the transport of
airborne particulate matter in
concentrations that caused an
exceedance or violation of the
NAAQS.11 States would be expected to
11 As discussed in rules proposed at 71 FR 2665–
2668, January 17, 2006, and 71 FR 2710 and 2731,
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control emissions from contributing
anthropogenic sources as appropriate
under the definition of the proposed
PM10–2.5 indicator.
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C. Stratospheric Ozone Intrusion
Consideration of stratospheric ozone
intrusions applies only to the 8-hour
ozone standard. The occurrence of such
inversions is extremely difficult to
measure or document given currently
measured meteorological parameters.
The infrequence, short duration, and
localized nature of such events makes it
difficult to use currently available,
general meteorological data, which are
usually collected at isolated locations
like airports, to determine whether a
stratospheric ozone intrusion has
occurred. The EPA believes it is
important to differentiate between
stratospheric ozone intrusion, which is
an exceptional event for the purpose of
flagging data, and other non-exceptional
meteorological events. Although data
have been identified in the past showing
the result of stratospheric ozone
intrusion, no standard definition or
criteria have been established for
concrete identification. Therefore, EPA’s
determination of whether a
stratospheric ozone intrusion has
occurred is a case-by-case decision
based on reasonable judgment
considering the season of the year; time
of day; persistence, duration, type and
severity of accompanying
meteorological conditions associated
with the ozone measurement in
question; and other data showing that
conditions were not conducive to local
high ozone production but for this
intrusion.
VII. Treatment of Fireworks Displays
While we are not including fireworks
displays in our proposed rule governing
exceptional events, we are proposing as
a policy matter to address certain
displays in a manner similar to
exceptional events. Some national and/
or cultural traditions, such as July 4th
Independence Day and Chinese New
Year, have long included fireworks
displays as important—indeed, many
might assert essential—elements of their
observances. While this issue is not
specifically covered in CAA section 319,
EPA believes that Congress did not
intend to require EPA to consider air
quality violations associated with such
cultural traditions in regulatory
2736–40, January 17, 2006, where properly sited
monitors show exceedances or violations of
proposed PM10–2.5 standards, it will generally be
presumed that such concentrations are due to
emissions of urban origin and therefore subject to
regulations, unless shown to be due to an
exceptional event.
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determinations to prohibit these
activities.
We are not aware of any information
showing adverse air quality impacts
caused by individual use of fireworks in
relatively small quantities. However,
analyses of monitoring data collected on
July 4th and July 5th indicates that large
fireworks displays, in combination with
other sources, can in some
circumstances be potentially significant
sources of air pollutant emissions. For
this reason, States are encouraged to
take reasonable precautions to minimize
exposures to emissions from fireworks
displays, as well as to manage
associated activities that may have
significant impact in the areas where
these events are held. Such actions may
include alerting the public to the
potential for short-term air quality
impacts that may result from the
discharge of fireworks at large displays,
monitoring prevailing winds, and
locating displays downwind of
concentrations of people. States are
encouraged, too, to explore the use of
lower-emitting fireworks, such as those
developed for frequent use at
amusement parks.
For these reasons, where States can
show that the use of fireworks displays
is integral to significant traditional
national, ethnic, or other cultural
events, we are proposing that air quality
data associated with such events could
be excluded. We request comments on
alternative approaches to addressing
emissions from fireworks at such events.
VIII. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), EPA must
determine whether the regulatory action
is ‘‘significant’’ and, therefore, subject to
the Office of Management and Budget
(OMB) review and the requirements of
the Executive Order. The order defines
‘‘significant regulatory action’’ as one
that is likely to result in a rule that may:
(1) Have an annual effect on the
economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
State, local, or Tribal governments or
communities;
(2) Create a serious inconsistency or
otherwise interfere with an action taken
or planned by another agency;
(3) Materially alter the budgetary
impact of entitlements, grants, user fees,
or loan programs or the rights and
obligations of recipients thereof; or
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(4) Rraise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Pursuant to the terms of Executive
Order 12866, it has been determined
that the proposed rule is a ‘‘significant
regulatory action.’’ As such, this
proposed rule was submitted to OMB
for review under Executive Order
12866.
B. Paperwork Reduction Act
This action does not impose an
information collection burden. The
information being requested under this
rule is consistent with current
requirements related to information
needed to verify the authenticity of
monitoring data submitted to EPA’s
AQS data base, and to justify data that
has been flagged as being affected by
exceptional or natural events. The OMB
has previously approved the
information collection requirements
contained in the existing regulations at
40 CFR part 58.01, subparts A through
E, under the provisions of the
Paperwork Reduction Act, 44 U.S.C.
3501 et seq. and assigned OMB control
number 2060–0084, EPA ICR number
940.17. A copy of the OMB approved
Information Collection Request (ICR)
may be obtained from Susan Auby,
Collection Strategies Division; U.S.
Environmental Protection Agency
(2822T); 1200 Pennsylvania Ave., NW.,
Washington, DC 20460 or by calling
(202) 566–1672.
Burden means that total time, effort,
or financial resources expended by
persons to generate, maintain, retain, or
disclose or provide information to or for
a Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information. An Agency
may not conduct or sponsor, and a
person is not required to respond to a
collection of information unless it
displays a currently valid OMB control
number. The OMB control numbers for
EPA’s regulations in the CFR are listed
in 40 CFR part 9.
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C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedures Act (APA) or
any other statute unless the EPA
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions. For the
purpose of assessing the impacts of
today’s proposed rule on small entities,
small entity is defined as: (1) A small
business that is a small industry entity
as defined in the U.S. Small Business
Administration (SBA) size standards.
(See 13 CFR 121); (2) a small
governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominate in its field.
Courts have interpreted the RFA to
require a regulatory flexibility analysis
only when small entities will be subject
to the requirements of the rule. See,
Michigan v. EPA, 213 F.3d 663, 668–69
(D.C. Cir., 2000), cert. den., 532 U.S. 903
(2001). This rule would not establish
requirements applicable to small
entities. Instead, this rule provides the
criteria necessary for State, local, or
Tribal air quality agencies to meet in
order to properly flag data as being
influenced by an exceptional or natural
event. The rule also provides
information concerning what action
should be taken by a State, local, or
Tribal air quality agency to protect
public health once EPA has provided a
concurrence on data that has been
flagged as being influenced by an
exceptional or natural event. Because
affected States would have discretion to
choose the sources that may need to be
regulated and the emissions reductions
each selected source would have to
achieve using RACM or BACM related
to anthropogenic sources in the area
determined to be influenced by an
exceptional or natural event, EPA could
not predict the effect of the rule on
small entities.
After considering the economic
impacts of today’s proposed rule on
small entities, I certify that this rule will
not have a significant economic impact
on a substantial number of small
entities.
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal Agencies to assess the effects of
their regulatory actions on State, local
and Tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State
governments, in the aggregate, or to the
private sector, of $100 million or more
in any 1 year. Before promulgating an
EPA rule for which a written statement
is needed, section 205 of the UMRA
generally requires EPA to identify and
consider a reasonable number of
regulatory alternatives and adopt the
least costly, most cost-effective or least
burdensome alternative that achieves
the objectives of the rule. The
provisions of section 205 do not apply
when they are inconsistent with
applicable law. Moreover, section 205
allows EPA to adopt an alternative other
than the least costly, most cost-effective
or least burdensome alternative if the
Administrator publishes with the final
rule an explanation of why that
alternative was not adopted. Before EPA
establishes any regulatory requirements
that may significantly or uniquely affect
small governments, including Tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments to have
meaningful and timely input in the
development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small government on compliance with
regulatory requirements.
Today’s action does not include a
Federal mandate within the meaning of
UMRA that may result in expenditures
of $100 million or more in any 1 year
by either State, local, or Tribal
governments in the aggregate or to the
private sector, and therefore, is not
subject to the requirements of sections
202 and 205 of the UMRA.
Inasmuch as this action simply
provides the criteria for State, local, or
Tribal air quality agencies to flag data to
be discounted for regulatory purposes
that is being influenced by exceptional
or natural events, this proposed Federal
action will not impose mandates that
will require expenditures of $100
million or more in the aggregate in any
1 year.
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, or the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’
This proposed rule does not have
federalism implications. It will not have
substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. The CAA
establishes the scheme whereby States
take the lead in developing plans to
meet the NAAQS. This rule will not
modify the relationship of the States
and EPA for purposes of developing
programs to implement the NAAQS.
Thus, Executive Order 13132 does not
apply to this rule.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
Tribal officials in the development of
regulatory policies that have Tribal
implications.’’ This proposed rule does
not have ‘‘Tribal implications’’ as
specified in Executive Order 13175. The
rule provides information concerning
what action should be taken by a State,
local, or Tribal air quality agency
implementing relevant air quality
programs to protect public health once
EPA has provided a concurrence on data
that has been flagged as being
influenced by an exceptional or natural
event. The CAA and the Tribal
Authority Rule (TAR) give Tribes the
opportunity to develop and implement
CAA programs, but it leaves to the
discretion of the Tribe whether to
develop these programs and which
programs, or appropriate elements of a
program, the Tribe will adopt.
This rule does not have Tribal
implications as defined by Executive
Order 13175. It does not have a
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substantial direct effect on one or more
Indian Tribes, because no Tribe has
implemented an air quality management
program related to the PM NAAQS at
this time. Furthermore, this rule does
not affect the relationship or
distribution of power and
responsibilities between the Federal
government and Indian Tribes. The
CAA and the TAR establish the
relationship of the Federal government
and Tribes in developing plans to attain
the NAAQS, and this rule does nothing
to modify that relationship. Because this
rule does not have Tribal implications,
Executive Order 13175 does not apply.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045: ‘‘Protection of
Children From Environmental Health
and Safety Risks’’ (62 FR 19885, April
23, 1997) applies to any rule that (1) is
determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health and safety risk
that EPA has reason to believe may have
a disproportionate effect on children. If
the regulatory action meets both criteria,
EPA must evaluate the environmental
health or safety effects of the planned
rule on children, and explain why the
planned regulation is preferable to other
potentially effective and reasonably
feasible alternatives considered by EPA.
This action is not subject to Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866, and because
EPA does not have reason to believe that
the environmental health risks or safety
risks addressed by this rule present a
disproportionate risk or safety risk to
children. The rule provides information
concerning what action should be taken
by a State, local, or Tribal air quality
agency to protect public health once
EPA has provided a concurrence on data
that has been flagged as being
influenced by an exceptional or natural
event.
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H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions that Significantly
Affect Energy Supply, Distribution, or
Use,’’ (66 FR 28355, May 22, 2001)
because it is not likely to have a
significant adverse effect on the supply,
distribution, or use of energy. Further,
we have concluded that this rule is not
likely to have any adverse energy
effects.
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I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer Advancement Act
of 1995 (NTTAA), Public Law No. 104–
113, section 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards (VCS) in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impracticable. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by VCS bodies. The NTTAA
directs EPA to provide Congress,
through OMB, explanations when EPA
decides not to use available and
applicable VCS.
This action does not involve technical
standards. Therefore, EPA did not
consider the use of any VCS.
List of Subjects in 40 CFR Parts 50 and
51
Environmental protection, Air
pollution control, National parks,
Wilderness areas.
Dated: March 1, 2006.
Stephen L. Johnson,
Administrator.
In consideration of the foregoing, the
Environmental Protection Agency
proposes to amend 40 CFR parts 50 and
51 as follows:
PART 50—NATIONAL PRIMARY AND
SECONDARY AMBIENT AIR QUALITY
STANDARDS
1. The authority citation for part 50
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
2. Amend § 50.1 to add paragraphs (j),
(k), and (l) to read as follows:
§ 50.1
Definitions.
*
*
*
*
*
(j) Exceptional event means an event
that 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 in accordance with
40 CFR 50.13 to be an exceptional event;
it does not include stagnation of air
masses or meteorological inversions; a
meteorological event involving high
temperatures or lack of precipitation; or
air pollution relating to source
noncompliance.
(k) Natural event means an event in
which human activity plays little or no
direct causal role.
(l) Exceedance with respect to a
national ambient air quality standard
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Frm 00018
Fmt 4701
Sfmt 4702
means one occurrence of a measured or
modeled concentration that exceeds the
specified concentration level of such
standard for the averaging period
specified by the standard.
3. Add § 50.14 to read as follows:
§ 50.14 Treatment of air quality monitoring
data influenced by exceptional events.
(a) Requirements. (1) A State may
request EPA to exclude data showing
exceedances or violations of the
national ambient air quality standards
that are directly due to an exceptional
event from use in determinations by
demonstrating to EPA’s satisfaction that
such event caused a specific air
pollution concentration at a particular
air quality monitoring location.
(2) Demonstrations may include any
reliable and accurate data, but must
demonstrate a clear causal relationship
between the measured exceedance or
violation of such standards and the
event.
(b) Determinations by EPA. (1) EPA
shall exclude data due to such event
from use in determinations where a
State demonstrates:
(i) That an exceptional event caused
a specific air pollution concentration
resulting in an exceedance or violation
of the national ambient air quality
standards at a particular air quality
monitoring location; and
(ii) That it has taken appropriate
actions to protect public health.
(2) [Reserved]
(c) Schedules and procedures—(1)
Public notification. (i) All States and,
where applicable, their political
subdivisions must notify the public
promptly whenever an event occurs or
is reasonably anticipated to occur which
may result in the exceedance of an
applicable air quality standard.
(ii) [Reserved]
OPTION 1 for paragraphs (c)(2)
through (c)(4):
(2) Flagging of data. (i) A State shall
notify EPA of its intent to exclude one
or more measured exceedances of an
applicable ambient air quality standard
as being due to an exceptional event by
placing a flag in the appropriate field for
the data record of concern in accordance
with the schedules for submission of
data to the AQS data base in 40 CFR
58.35.
(ii) Flags placed on data in accordance
with this section shall be deemed
informational only, and the data shall
not be excluded from determinations
with respect to exceedances or
violations of the national ambient air
quality standards unless and until EPA
notifies the State of its concurrence by
placing a concurrence flag in the
appropriate field for the data record in
the AQS data base.
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(3) Submission of demonstrations. (i)
A State that has flagged data as being
due to an exceptional event shall, after
notice and opportunity for public
comment, submit a complete
demonstration to EPA in support of its
request for exclusion not later than 180
days following the end of the calendar
quarter in which the flagged
concentration was recorded.
(A) Extensions. Where a State
demonstrates to the satisfaction of EPA
that additional time is needed to obtain
information or complete analyses to
demonstrate that an exceptional event
caused an exceedance or violation of an
ambient air quality standard, and that
such information is likely to have
significant probative value, then EPA
may grant an extension of the date for
submission of demonstrations of not
more than an additional 90 days.
(B) [Reserved]
(ii) [Reserved]
(4) EPA review and concurrence or
nonconcurrence. (i) EPA shall complete
its review and concur or nonconcur
with a State’s request for exclusion not
later than 30 days following receipt of
a complete submission from the State.
EPA shall notify the State of its
concurrence or nonconcurrence by
placing a flag in the appropriate field for
the data record in the AQS data base.
(A) Extensions. Where additional time
is needed to complete its review of the
State’s demonstration, EPA may extend
the time for review by not more than an
additional 30 days.
(B) [Reserved]
(ii) [Reserved]
OPTION 2 for paragraphs (c)(2)
through (c)(4):
(2) Flagging of data. (i) A State shall
notify EPA of its intent to exclude one
or more measured exceedances of an
applicable ambient air quality standard
as being due to an exceptional event by
placing a flag in the appropriate field for
the data record of concern in accordance
with the schedules for submission of
data to the AQS data base in 40 CFR
58.35.
(ii) Flags placed on data in accordance
with this section shall be deemed
informational only, and the data shall
not be excluded from determinations
with respect to exceedances or
violations of the national ambient air
quality standards unless and until EPA
notifies the State of its concurrence by
placing a concurrence flag in the
appropriate field for the data record in
the AQS data base.
(3) Submission of demonstrations. (i)
A State that has flagged data as being
due to an exceptional event shall, after
notice and opportunity for public
comment, submit a complete
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demonstration to EPA in support of its
request for exclusion not later than 3
years following the end of the calendar
quarter in which the flagged
concentration was recorded.
(ii) [Reserved]
(4) EPA review and concurrence or
nonconcurrence. (i) EPA shall complete
its review and concur or nonconcur
with a State’s request for exclusion not
later than 30 days following receipt of
a complete submission from the State.
EPA shall notify the State of its
concurrence or nonconcurrence by
placing a flag in the appropriate field for
the data record in the AQS data base.
(A) Extensions. Where additional time
is needed to complete its review of the
State’s demonstration, EPA may extend
the time for review by not more than an
additional 30 days.
(B) [Reserved]
(ii) [Reserved]
OPTION 3 for paragraphs (c)(2)
through (c)(4):
(2) Flagging of data. (i) A State shall
notify EPA of its intent to exclude one
or more measured exceedances of an
applicable ambient air quality standard
as being due to an exceptional event by
placing a flag in the appropriate field for
the data record of concern not later than
180 days prior to the date on which EPA
intends to propose determinations with
respect to violations of applicable
national ambient air quality standards.
(ii) Flags placed on data in accordance
with this section shall be deemed
informational only, and the data shall
not be excluded from determinations
with respect to exceedances or
violations of the national ambient air
quality standards unless and until EPA
notifies the State of its concurrence by
placing a concurrence flag in the
appropriate field for the data record in
the AQS data base.
(3) Submission of demonstrations. (i)
A State that has flagged data as being
due to an exceptional event shall, after
notice and opportunity for public
comment, submit a complete
demonstration to EPA in support of its
request for exclusion not later than 180
days prior to the date on which EPA
intends to propose determinations with
respect to violations of applicable
national ambient air quality standards.
(ii) [Reserved]
(4) EPA review and concurrence or
nonconcurrence. (i) EPA shall complete
its review and concur or nonconcur
with a State’s request for exclusion not
later than 30 days following receipt of
a complete submission from the State.
EPA shall notify the State of its
concurrence or nonconcurrence by
placing a flag in the appropriate field for
the data record in the AQS data base.
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Fmt 4701
Sfmt 4702
12609
(A) Extensions. Where additional time
is needed to complete its review of the
State’s demonstration, EPA may extend
the time for review by not more than an
additional 30 days.
(B) [Reserved]
(ii) [Reserved]
PART 51—NATIONAL PRIMARY AND
SECONDARY NATIONAL AMBIENT AIR
QUALITY STANDARDS
1. The authority citation for part 51
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
2. Add Subpart Y consisting of
§ 51.920 to read as follows:
Subpart Y—Exceptional Events
OPTION 1 for § 51.920:
§ 51.920
Mitigation of exceptional events.
(a) As a condition for EPA’s approval
of a request to exclude air quality data
due to exceptional events from use, each
State must take appropriate and
reasonable actions to protect public
health from exceedances or violations of
the national ambient air quality
standards due to exceptional events.
The State must:
(1) Provide for prompt public
notification whenever air quality
concentrations exceed or are expected to
exceed an applicable ambient air quality
standard.
(2) Provide for public education
concerning actions that individuals may
take to reduce exposures to unhealthy
levels of air quality during and
following an exceptional event.
(3) Provide for the implementation of
reasonable measures to protect public
health from exceedances or violations of
ambient air quality standards caused by
exceptional events.
(a) [Reserved]
OPTION 2 for § 51.920:
§ 51.920
Mitigation of exceptional events.
(a) As a condition for EPA’s approval
of a request to exclude air quality data
due to exceptional events from use, each
plan must include a mitigation action
plan which provides for appropriate
actions to protect public health from
exceedances or violations of the
national ambient air quality standards
due to exceptional events. Each
mitigation action plan must:
(1) Provide for prompt public
notification whenever air quality
concentrations exceed or are expected to
exceed an applicable ambient air quality
standard.
(2) Provide for public education
concerning actions that individuals may
take to reduce exposures to unhealthy
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Federal Register / Vol. 71, No. 47 / Friday, March 10, 2006 / Proposed Rules
levels of air quality during and
following an exceptional event.
(3) Describe the procedures by which
appropriate actions will be identified
and taken to prevent or mitigate public
health threats associated with
exceptional events.
(4) Provide for the implementation of
reasonably available control measures to
reduce emissions from those
anthropogenic sources which are not
exempt under § 50.13(a)(2)(ii) of this
chapter and which interact with
recurring natural events to contribute to
exceedances or violations of applicable
national ambient air quality standards.
(b) States should periodically
reevaluate mitigation action plans for
adequacy and revise them as necessary
and appropriate.
OPTION 3 for § 51.920:
§ 51.920
Mitigation of exceptional events.
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(a) As a condition for EPA’s approval
of a request to exclude air quality data
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due to exceptional events from use in
determinations with respect to
exceedances or violations of the
national ambient air quality standards,
each State must adopt and implement a
mitigation action plan for an affected
area which provides for appropriate
actions to protect public health from
exceedances or violations of national
ambient air quality standards due to
exceptional events which is to be
implemented in an affected area on an
episodic basis. Mitigation action plans
need not be incorporated into the
applicable implementation plan, but
each mitigation action plan must:
(1) Provide for prompt public
notification whenever air quality
concentrations exceed or are expected to
exceed an applicable ambient air quality
standard.
(2) Provide for public education
concerning actions that individuals may
take to reduce exposures to unhealthy
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Fmt 4701
Sfmt 4702
levels of air quality during and
following an exceptional event.
(3) Describe the procedures by which
appropriate actions will be identified
and taken to prevent or mitigate public
health threats associated with
exceptional events.
(4) Provide for the implementation of
reasonably available control measures to
reduce emissions from those
anthropogenic sources which are not
exempt under § 50.13(a)(2)(ii) of this
chapter and which interact with
recurring natural events to contribute to
exceedances or violations of applicable
national ambient air quality standards.
(b) States should periodically
reevaluate mitigation action plans for
adequacy and revise them as necessary
and appropriate.
[FR Doc. 06–2179 Filed 3–9–06; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 71, Number 47 (Friday, March 10, 2006)]
[Proposed Rules]
[Pages 12592-12610]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-2179]
[[Page 12591]]
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Part V
Environmental Protection Agency
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40 CFR Parts 50 and 51
The Treatment of Data Influenced by Exceptional Events; Proposed Rule
Federal Register / Vol. 71, No. 47 / Friday, March 10, 2006 /
Proposed Rules
[[Page 12592]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 50 and 51
[EPA-HQ-OAR-2005-0159; FRL-8042-5]
RIN 2060-AN40
The Treatment of Data Influenced by Exceptional Events
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: Today, EPA is proposing a rule to govern the review and
handling of air quality monitoring data influenced by exceptional
events. Exceptional events are events for which the normal planning and
regulatory process established by the Clean Air Act (CAA) is not
appropriate. In this rulemaking action, EPA is proposing to: Implement
section 319(b)(3)(B) and section 107(d)(3) authority to exclude air
quality monitoring data from regulatory determinations related to
exceedances or violations of the National Ambient Air Quality Standards
(NAAQS) and avoid designating an area as nonattainment, redesignating
an area as nonattainment, or reclassifying an existing nonattainment
area to a higher classification if a State adequately demonstrates that
an exceptional event has caused an exceedance or violation of a NAAQS.
Also, EPA is proposing four options with respect to whether, and to
what extent, States should be required to take additional actions to
address public health impacts related to the event.
DATES: Comments must be received on or before May 9, 2006. Comments
must be postmarked by the last day of the comment period.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2005-0159, by one of the following methods:
https://www.regulations.gov. Follow the on-line
instructions for submitting comments.
E-mail: Comments may be sent by electronic mail (e-mail)
to A-and-R-Docket@epa.gov, Attention Docket ID No. EPA-HQ-OAR-2005-
0159.
Fax: Fax your comments to: 202-566-1741, Attention Docket
ID no. EPA-HQ-OAR-2005-0159.
Mail: Send your comments to: Air and Radiation Docket and
Information Center, U.S. Environmental Protection Agency, Mail Code:
6102T, 1200 Pennsylvania Ave., NW., Washington, DC 20460, Attention
Docket ID No. EPA-HQ-OAR-2005-0159.
Hand Delivery: Air and Radiation Docket and Information
Center, U.S. Environmental Protection Agency, 1301 Constitution Avenue,
NW., Room B102, Washington, DC, Attention Docket ID No. EPA-HQ-OAR-
2005-0159. 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. EPA-HQ-OAR-
2005-0159. 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 information through
https://www.regulations.gov, or e-mail. The https://www.regulations.gov
Web site is an ``anonymous access'' system, which means that 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 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. For additional instructions on submitting
comments, go to SUPPLEMENTARY INFORMATION.
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 Office of Air and
Radiation Docket and Information Center, EPA West, Room B102, 1301
Constitution Ave., NW., Washington, DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal
holidays. The telephone number for the Public Reading Room is (202)
566-1744, and the telephone number for the Office of Air and Radiation
Docket and Information Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: General questions concerning this
proposed rule should be addressed to Mr. Larry D. Wallace, Ph.D.,
Office of Air Quality Planning and Standards, Air Quality Policy
Division, Mail Code C539-01, Research Triangle Park, NC 27711;
telephone (919) 541-0906, and e-mail address wallace.larry@epa.gov.
Questions concerning technical and analytical issues related to
this proposed rule should be addressed to Mr. Neil Frank, Office of Air
Quality Planning and Standards, Air Quality Assessment Division, Mail
Code C304-04, Research Triangle Park, NC 27711; telephone (919) 541-
5560, and e-mail address frank.neil@epa.gov.
SUPPLEMENTARY INFORMATION:
Public Hearing
The EPA will hold two public hearings on today's proposal during
the comment period. The details of the public hearings, including the
times, dates, and locations will be provided in a future Federal
Register notice. The public hearings will provide interested parties
the opportunity to present data, views, or arguments concerning the
proposed rule. The EPA may ask clarifying questions during the oral
presentations, but will not respond to the presentations or comments at
that time. Written statements and supporting information submitted
during the comment period will be considered with the same weight as
any oral comments and supporting information presented at the public
hearings. Under CAA section 307(d)(1)(A), the procedural requirements
of section 307(d) apply to this proposal. In addition, under section
307(d)(1)(U), the Administrator determines that this action is subject
to the provisions of section 307(d). Section 307(d)(1)(U) provides that
the provisions of section 307(d) apply to ``such other actions as the
Administrator may determine.'' The EPA is including the proposals in
today's proposed rulemaking under sections 307(d)(1)(A) and (U).
Comments
1. Submitting CBI. Do not submit this information to EPA 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
[[Page 12593]]
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.
2. Tips for Preparing Your Comments. When submitting comments,
remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions--The agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your cost estimate in sufficient detail to allow for it
to be reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
In addition, please send a copy of your comments to: Mr. Larry D.
Wallace, Ph.D., U.S. Environmental Protection Agency, by one of the
means listed below:
1. E-Mail: wallace.larry@epa.gov.
2. Fax: (919) 541-5489, Attention: Mr. Larry D. Wallace, Ph.D.
3. Mail: Mr. Larry D. Wallace, Ph.D., U.S. Environmental Protection
Agency, Office of Air Quality Planning and Standards, Mail Code: C539-
01, Research Triangle Park, NC 27711.
4. Hand Delivery: Mr. Larry D. Wallace, Ph.D., U.S. Environmental
Protection Agency, Office of Air Quality Planning and Standards, 109
T.W. Alexander Drive, Research Triangle Park, NC 27709.
Table of Contents
The following is an outline of the preamble.
I. Preamble Glossary of Terms and Acronyms
II. Background and Purpose of Today's Rulemaking
A. Legislative Requirements
B. Historical Experience Concerning Exceptional and Natural
Events
III. Today's Proposed Action
A. To Whom and to What Pollutants Does Today's Proposed Rule
Apply?
B. How Does This Rule Relate to Indian Tribes?
C. What Is an Exceptional Event?
D. Examples of Exceptional Events
1. Chemical Spills and Industrial Accidents
2. Structural Fires
3. Exceedances Due to Transported Pollution
4. Exceedances Due to a Terrorist Attack
5. Natural Events
a. Volcanic and Seismic Activities
b. Natural Disasters and Associated Clean-up Activities
c. High Wind Events
d. Unwanted Fires
e. Stratospheric Ozone Intrusions
IV. The Management of Air Quality Data Affected by Exceptional
Events
A. Flagging of Data in the AQS Database
B. What Does It Mean for an Event To ``Affect Air Quality''?
1. Option 1: 95th Percentile Criterion
2. Option 2: 75th Percentile/95th Percentile Tiered Approach
3. Option 3: Case-by-Case Approach Based On Weight of Evidence
C. Use of a ``But For'' Test
D. Schedules and Procedures for Flagging and Requesting
Exclusion of Data
1. Option 1: Early Data Flagging and Demonstration Submission
2. Option 2: Early Data Flagging and Delayed Demonstration
Submission
3. Option 3: Delayed Data Flagging and Demonstration Submission
E. Exclusion of Entire 24-Hour Value as Opposed to a Partial
Adjustment of the 24-Hour Value
F. What Should States be Required To Submit in Their Exceptional
Events Demonstrations?
G. Special Considerations Relevant to Proposed Standards for
PM10-2.5
H. Public Availability of Air Quality Data and Demonstrations
Related to Exceptional Events
V. Additional Requirements
A. Option 1: Proposed Option: Require Public Notification,
Education and Appropriate and Reasonable Measures
B. Option 2: The Development of a Mitigation Plan by States
Under Section 110 of the CAA
C. Option 3: The Development of a Mitigation Plan for Episodic
Events
D. Option 4: Do Not Require States To Adopt and Implement
Specific Mitigation Plans or Measures Under This Rule
VI. Special Treatment of Certain Events Under This Rule
A. Volcanic and Seismic Activities
B. High Wind Events
C. Stratospheric Ozone Intrusion
VII. Treatment of Fireworks Displays
VIII. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions that Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer Advancement Act
I. Preamble Glossary of Terms and Acronyms
The following are abbreviations of terms used in the preamble.
AQS Air Quality System
BACM Best Available Control Measures
CAA Clean Air Act
CAAA Clean Air Act Amendments
EPA Environmental Protection Agency
FIP Federal Implementation Plan
FMP Fire Mitigation Plan
NAAQS National Ambient Air Quality Standards
NEAP Natural Event Action Plan
OAQPS Office of Air Quality Planning and Standards
PM10 Particles with a nominal mean aerodynamic diameter less
than or equal to 10 micrometers
PM10-2.5 Particles with a nominal mean aerodynamic diameter
greater than 2.5 micrometers and less than or equal to 10 micrometers
PM2.5 Particles with a nominal mean aerodynamic diameter
less than or equal to 2.5 micrometers
RACM Reasonably Available Control Measures
SIP State Implementation Plan
SAFE-TEA-LU Safe Accountable Flexible Efficient-Transportation Equity
Act--A Legacy for Users
SMP Smoke Management Plan
TAR Tribal Authority Rule
TIP Tribal Implementation Plan
II. Background and Purpose of Today's Rulemaking
A. Legislative Requirements
Today, EPA is proposing a rule to govern the review and handling of
air quality monitoring data influenced by exceptional events. As
discussed below, these are events for which the normal planning and
regulatory process established by the CAA is not appropriate. Section
319 of the CAA, as amended by section 6013 of the Safe Accountable
Flexible Efficient-Transportation Equity Act: A Legacy for Users (SAFE-
TEA-LU) of 2005, requires EPA to publish this rule in the Federal
[[Page 12594]]
Register no later than March 1, 2006.\1\ Further, EPA is required to
issue the final rule no later than 1 year from the date of proposal.
---------------------------------------------------------------------------
\1\ All subsequent references to section 319 of the CAA in this
proposal are to section 319 as amended by SAFE-TEA-LU unless
otherwise noted.
---------------------------------------------------------------------------
The EPA is proposing to establish procedures and criteria related
to the identification, evaluation, interpretation, and use of air
quality monitoring data related to any NAAQS where States petition EPA
to exclude data that are affected by exceptional events. Section 319
defines an event as an exceptional event if the event affects air
quality; 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 statutory definition of
exceptional event specifically excludes stagnation of air masses or
meteorological inversions; a meteorological event involving high
temperature or lack of precipitation; or air pollution relating to
source noncompliance.
Section 319(b)(3)(B)(i) requires a State air quality agency to
demonstrate through ``reliable, accurate data that is promptly
produced'' that an exceptional event occurred.\2\ Section
319(b)(3)(B)(ii) requires that ``a clear causal relationship'' be
established between a measured exceedance of a NAAQS and the
exceptional event demonstrating ``that the exceptional event caused a
specific air pollution concentration at a particular location.'' In
addition, section 319(b)(3)(B)(iii) requires a public process to
determine whether an event is an exceptional event. Finally, section
319(b)(3)(B)(iv) requires criteria and procedures for a Governor to
petition the Administrator to exclude air quality monitoring data that
is directly due to exceptional events from use in determinations with
respect to exceedences or violations of the NAAQS.
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\2\ While this document refers primarily to States as the entity
responsible for flagging data impacted by exceptional events, other
agencies, such as local or Tribal government agencies, may also have
standing to flag data as being affected by these types of events,
and the criteria and procedures that are discussed in this
rulemaking also apply to these entities.
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Section 319 also contains a set of five principles for EPA to
follow in developing regulations to implement section 319:
(i) Protection of public health is the highest priority;
(ii) Timely information should be provided to the public in any
case in which the air quality is unhealthy;
(iii) All ambient air quality data should be included in a timely
manner in an appropriate Federal air quality data base that is
accessible to the public;
(iv) Each State must take necessary measures to safeguard public
health regardless of the source of the air pollution; and
(v) Air quality data should be carefully screened to ensure that
events not likely to recur are represented accurately in all monitoring
data and analyses (42 U.S.C. 7619(b)(3)(A)).
In adopting revisions to section 319, EPA believes that Congress
sought to provide statutory relief to States to allow them to avoid
being designated as nonattainment or to avoid continuing to be
designated nonattainment as a result of exceptional events in
appropriate circumstances. In addition, Congress indicated that States
should not have to prepare and implement regulatory strategies when
their air quality is affected by events beyond their reasonable
control. To accomplish this goal, Congress enumerated certain minimum
requirements for this rulemaking. In addition, Congress provided
certain statutory principles for EPA to follow in promulgating
regulations to exclude data affected by exceptional events.
Section 319 also includes an interim provision, section 319(b)(4),
that addresses the transition period between the present and the date
that a final regulation governing the treatment of data related to
exceptional events is promulgated. The provision indicates that
following EPA guidance documents continues to apply until the effective
date of a final regulation promulgated under section 319(b)(2):
``Guidance on the Identification and Use of Air Quality Data Affected
by Exceptional Events'' (July 1986); ``Areas Affected by
PM10 Natural Events,'' May 30, 1996; and appendices I, K,
and N to 40 CFR part 50, which describe how air quality monitoring data
are to be used and interpreted to determine compliance with the
applicable NAAQS. The statute requires the promulgation of the final
rule no later than 1 year following the publication of this proposed
rule.
B. Historical Experience Concerning Exceptional and Natural Events
Since 1977, EPA guidance and regulations have either implied or
documented the need for a flagging system for data affected by an
exceptional event. The first EPA guidance related to the exclusion or
discounting of data affected by an exceptional event was an Office of
Air Quality Planning and Standards (OAQPS) guidance document entitled,
``Guidelines for the Interpretation of Air Quality Standards,''
Guideline No. 1.2-008 (revised February 1977).\3\
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\3\ ``Guideline for Interpretation of Air Quality Standards,''
U.S. Environmental Protection Agency, Office of Air Quality Planning
and Standards, Research Triangle Park, N.C. OAQPS No. 1.2-008
(Revised February 1977). The guidance indicated the need for a data
flagging system which would require the submittal of detailed
information establishing that a violation was due to uncontrollable
natural sources and that the information could be used in decision-
making related to the feasibility of modifying control strategies.
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In July 1986, EPA issued the guidance entitled, ``Guideline on the
Identification and Use of Air Quality Data Affected by Exceptional
Events'' (the Exceptional Events Policy). The Exceptional Events Policy
provided criteria for States to use in making decisions related to
identifying data that have been influenced by an exceptional event.
In addition to the Exceptional Events Policy, on July 1, 1987, EPA
promulgated the NAAQS for PM10 (particulate matter with an
aerodynamic diameter of 10 micrometers or less) which also addressed
the issue of excluding or discounting data affected by exceptional
events.\4\ Appendix K of that rule allows for special consideration of
data determined to be affected by an exceptional event. Section 2.4 of
appendix K authorizes EPA to discount from consideration in making
attainment or nonattainment determinations for air quality data that
are attributable to ``an uncontrollable event caused by natural
sources'' of PM10, or ``an event that is not expected to
recur at a given location.'' Section 2.4 of appendix K, together with
EPA guidance contained in the Exceptional Events Policy, describes the
steps that should be taken for flagging PM10 data that a
State believes are affected by an exceptional or natural event.
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\4\ Federal Register (52 FR 24667), July 1, 1987.
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In 1990, section 188(f) was added to the CAA. This section of the
CAA provided EPA authority to waive either a specific attainment date
or certain planning requirements for serious PM10
nonattainment areas that were affected by nonanthropogenic sources. In
response to section 188(f), and in consideration of the CAA
consequences for areas affected by elevated concentrations caused by
natural events, in 1996 EPA issued a policy to address data affected by
natural events entitled, ``Areas Affected by PM10 Natural
Events,'' (the PM10 Natural Events Policy).\5\
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\5\ Memorandum from Mary D. Nichols, Assistant Administrator for
Air and Radiation, to EPA Regional Offices entitled, ``Areas
Affected by PM10 Natural Events,'' May 30, 1996.
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[[Page 12595]]
On July 18, 1997, EPA issued revised NAAQS for ozone and a new
NAAQS addressing PM2.5. For ozone, the revised NAAQS
provided for an 8-hour averaging period (versus 1 hour for the previous
NAAQS), and the level of the standard was changed from 0.12 ppm to 0.08
ppm (62 FR 38856). For the PM2.5 NAAQS, EPA established both
a new 24-hour standard and a new annual standard. In that Federal
Register, EPA also promulgated appendices I and N to 40 CFR part 50.
Appendices I and N provided the methodologies for determining whether
an area is in attainment of the 8-hour ozone and PM2.5 NAAQS
respectively, using ambient air quality data. Section 1.0 of appendix
I, and section 1.0(b) of appendix N provide the authority for EPA to
give special consideration to data determined to be affected by an
exceptional or natural event.
Appendices K, I, and N, which are a part of the NAAQS for the
affected pollutants as described above, provide that, while States must
submit all valid ambient air quality data to EPA's Air Quality System
(AQS) data base for use in making regulatory decisions, in some cases
it may be appropriate for the Regional Administrator to exclude,
discount, weight, or make adjustments to data that have been
appropriately flagged from calculations in determining whether or not
an area has attained the standard. These decisions are to be made on a
case-by-case basis using all available information related to the event
in question, and are required to be made available to the public for
review. It should also be noted that, while it would be desirable to be
able to adjust the daily value to exclude only those portions of the
data that are attributable to the exceptional event, due to technical
limitations, such subtraction has not been possible, and EPA's
historical practice has been to exclude a daily measured value in its
entirety when that value is found to be largely caused by an
exceptional event.
Following the promulgation of the 8-hour ozone and the
PM2.5 NAAQS, EPA provided additional guidance to States on
how to address data affected by exceptional and natural events.\6\ That
guidance directed the States to follow three specific EPA guidance
documents in making determinations related to data influenced by
exceptional and natural events: (1) The Exceptional Events Policy; (2)
The PM10 Natural Events Policy; and (3) The Interim Air
Quality Policy on Wildland and Prescribed Fires, Memorandum from
Richard D. Wilson, Acting Assistant Administrator for Air and
Radiation, to EPA Regional Administrators, May 15, 1998. The Interim
Air Quality Policy on Wildland and Prescribed Fires addressed the
treatment of air quality monitoring data that are affected by wildland
and prescribed fires that are managed for resource benefits.\7\ The EPA
will continue to use these policies to address issues related to the
existing and/or revised PM2.5 NAAQS pending EPA's final
action on today's proposed rulemaking. Similarly, issues related to
exceptional and natural events affecting the ozone standard will
continue to be addressed under the 1986 Exceptional Events Policy until
EPA issues a final exceptional events rule.
---------------------------------------------------------------------------
\6\ ``Guideline on Data Handling Conventions for the PM NAAQS,''
United States Environmental Protection Agency, Office of Air Quality
Planning and Standards, Research Triangle Park, N.C. 27711, EPA-454/
R-99-008, April 1999.
``Guideline on Data Handling Conventions for the 8-hour Ozone
NAAQS,'' United States Environmental Protection Agency, Office of
Air Quality Planning and Standards, Research Triangle Park, N.C.
27711, EPA-454/R-99-008, April 1999.
\7\ Following the promulgation of this rule, EPA will revise the
``Interim Air Quality Policy on Wildland and Prescribed Fires'' to
be consistent with current policies related to wildland and
prescribed fires as well as the final rulemaking on exceptional
events.
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III. Today's Proposed Action
A. To Whom and to What Pollutants Does Today's Proposed Rule Apply?
Under the statutory scheme established by the CAA, States are
primarily responsible for the administration of air quality management
programs within their borders. This includes the monitoring and
analysis of ambient air quality and submission of monitoring data to
EPA, which are then stored in EPA's AQS data base. The EPA retains an
important oversight responsibility for ensuring compliance with CAA
requirements. With respect to the treatment of air quality monitoring
data, States are responsible for ensuring data quality and validity and
for identifying measurements that they believe warrant special
consideration, while EPA is responsible for reviewing and approving or
disapproving any requests for such consideration. Therefore, if
adopted, today's proposed rule would apply to all States; to local air
quality agencies to whom a State has delegated relevant
responsibilities for air quality management, including air quality
monitoring and data analysis; and, as discussed below, to Tribal air
quality agencies where appropriate. This proposed rule would also
govern EPA's actions in reviewing and approving or disapproving the
relevant actions taken or requested by States. Where EPA implements air
quality management programs on Tribal lands, this proposed rule would
govern those actions as well.
At present, only the NAAQS for ozone and PM contain provisions
which allow for the special handling of air quality data affected by
exceptional events (40 CFR part 50, appendices K, I, and N). The
language of section 319 of the CAA is broad in terms of making its
provisions applicable to events that ``affect air quality'' and to
exceedances or violations of ``the national ambient air quality
standards'' (42 U.S.C. 7619(b)(1)(A)(i), (b)(3)(B)(iv)). Thus, its
provisions can apply to the NAAQS for any criteria pollutant. Because
the NAAQS established for other criteria pollutants do not currently
contain provisions permitting the discounting or exclusion of data due
to exceptional events, we are proposing to only apply the provisions of
this rule initially to ozone and PM. As we review and consider the need
for revisions to the NAAQS for other pollutants, we will include
provisions to address exceptional events in those NAAQS in accordance
with section 319, as appropriate at that time. Because issuance of a
new or revised NAAQS will necessitate the initiation of the designation
process, EPA believes that the NAAQS rules are an appropriate place to
make provision for exceptional events in the evaluation of air quality
data. In the interim, where exceptional events result in exceedances or
violations of NAAQS that do not currently provide for special treatment
of the data, we intend to use our discretion as outlined under section
107(d)(3) not to redesignate affected areas as nonattainment based on
these events.
B. How Does This Rule Relate to Indian Tribes?
Under the CAA and the Tribal Authority Rule (TAR), eligible Indian
Tribes may develop and submit Tribal Implementation Plans (TIPs) for
EPA approval, to administer requirements under the CAA on their
reservations and other areas under their jurisdiction. However, Tribes
are not required to develop TIPs or otherwise implement relevant
programs under the CAA. The EPA has stated that it will continue to
ensure the protection of air quality throughout the nation, including
in Indian country, and will issue Federal Implementation Plans (FIPs)
as necessary or appropriate to fill gaps in program implementation in
affected areas of Indian country (63 FR 7254, 7265; February 12, 1998).
[[Page 12596]]
In cases where a Tribal air quality agency has implemented an air
quality monitoring network which is affected by emissions from
exceptional events, the criteria and procedures identified in this
proposed rule may be used to exclude or discount data for regulatory
purposes. Certain Tribes may implement all relevant components of an
air quality program for purposes of meeting the various requirements of
this proposed rule. In some cases, however, a Tribe may implement only
portions of the relevant program and may not be in a position to
address each of the procedures and requirements associated with
excluding or discounting emissions data (e.g., a particular Tribe may
operate a monitoring network for purposes of gathering and identifying
appropriate data, but may not implement relevant programs for the
purpose of mitigating the effects of exceptional events required under
this proposed rule). The EPA intends to work with Tribes on the
implementation of this proposed rule, which may include appropriate
implementation by EPA of program elements ensuring that any exclusion
or discounting of data in Indian country areas with air quality
affected by exceptional events comports with the procedures and
requirements of this proposed rule.
C. What Is an Exceptional Event?
In accordance with the language in section 319, EPA is proposing to
define the term ``exceptional event'' to mean an event that:
(i) Affects air quality;
(ii) Is not reasonably controllable or preventable;
(iii) Is an event caused by human activity that is unlikely to
recur at a particular location or a natural event; and
(iv) Is determined by the Administrator through the process
established in these regulations to be an exceptional event.
It is important to note that natural events, which are one form of
exceptional events according to this definition, may recur, sometimes
frequently (e.g., western wildfires). For purposes of this rule, EPA is
proposing to define ``natural event'' as an event in which human
activity has no substantial or direct causal connection to the event in
question. We recognize that over time, certain human activities may
have had some impact on the conditions which later give rise to a
``natural'' air pollution event. However, we do not believe that small
historical human contributions should preclude an event from being
deemed ``natural.''
In this proposed rule, EPA also defines the term ``exceedance''
with respect to compliance with the NAAQS and establishes criteria for
determining when an event can be said to ``affect air quality.'' We are
not proposing more detailed requirements for determining when an event
is ``not reasonably controllable or preventable'' because we believe
that such determinations will necessarily be dependent on specific
facts and circumstances that cannot be prescribed by rule. In adopting
section 188(f) of subpart 4 of the 1990 amendments to the CAA, Congress
recognized and provided for distinctions between these types of
activities, while discussing circumstances under which events should or
should not be considered natural (see Public Law 101-549, CAA
Amendments of 1990 House Report No. 101-290(l), May 17, 1990; and
discussion of Mono Lake, California therein).
D. Examples of Exceptional Events
The EPA believes that the following types of events meet the
definition of exceptional events, as defined above. This means that air
quality data affected by these types of events may qualify for
exclusion under this proposed rule if all other requirements of the
rule are met. The AQS data base also contains a more detailed list of
other similar events that may be flagged for special consideration
(https://www.epa.gov/ttn/airs/airsaqs/manuals/codedescs.htm).
1. Chemical Spills and Industrial Accidents
Emissions that result from accidents such as fires, explosions,
power outages, train derailments, vehicular accidents, or combinations
of these may be flagged as an exceptional event.
2. Structural Fires
Structural fires include any accidental fire involving a manmade
structure.
3. Exceedances Due to Transported Pollution
Transported pollution, whether national or international in origin
and whether from natural or anthropogenic sources, may cause
exceedances which are eligible for exclusion under this rule as long as
the other criteria and requirements for exceptional events under this
rule are met. For example, States may flag, and EPA may exclude, data
associated with fires occurring outside of the borders of the United
States, such as forest fires in Mexico, Central America, and Canada; or
transport events such as African dust and Asian dust which contribute
significantly to ambient concentrations of a pollutant, leading to
exceedances or violations of the NAAQS. An example of interstate
transported emissions which may be flagged as due to an exceptional
event would be emissions due to smoke from wildland fires which cause
exceedances or violations at monitoring sites in other States. Other
types of events may be considered on a case-by-case basis.
4. Exceedances Due to a Terrorist Attack
Emissions that result from a terrorist attack such as smoke from
fires, dust, explosions, power outages, train derailments, vehicular
accidents, or combinations of these may be flagged as an exceptional
event.
5. Natural Events
The natural events addressed by this proposed rule are: (1)
Volcanic and seismic activities; (2) natural disasters and associated
cleanup activities; (3) high wind events; (4) unwanted fires; and (5)
stratospheric ozone intrusions. The EPA will consider other types of
natural events on a case-by-case basis.
a. Volcanic and Seismic Activities. Ambient concentrations of
particulate matter for which volcanic eruptions or seismic activity
caused or contributed to high levels of particulate matter in an
affected area will be treated as natural events. While not occurring
frequently, volcanic and seismic activity can affect air quality data
related to the particulate matter NAAQS for an extended period of time
after an event. Volcanic eruptions contribute to ambient concentrations
in two ways; concentrations due to primary emissions (e.g., ash); and
emissions of precursor pollutants (e.g., sulfur dioxide) that
contribute to the secondary formation of particulate matter. Seismic
activity (e.g., earthquakes) can also contribute to ambient particulate
matter concentrations by shaking the ground, causing structures to
collapse and otherwise raising dust.
b. Natural Disasters and Associated Clean-up Activities. For the
purpose of flagging, major natural disasters, such as hurricanes and
tornados for which State, local, or Federal relief has been granted,
and clean-up activities associated with these events may be considered
exceptional events.
c. High Wind Events. High wind events are events that affect
ambient particulate matter concentrations through re-entrainment of
material, i.e., by raising dust. Concentrations of coarse particles,
i.e., PM10-2.5 and PM10 in some locations, are
most likely affected by these types of events, although
PM2.5
[[Page 12597]]
standards may be exceeded under such circumstances as well.
d. Unwanted Fires. Ambient particulate matter concentrations caused
by smoke from wildland fires will be treated as due to natural events
if the fires are determined to be unwanted fires, designated wildland
fire use fires, not designated or managed as prescribed fires, or
requiring appropriate suppression action by a wildland manager.\8\
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\8\ It should be noted that this rule does not cover
agricultural burning. To the extent that it is necessary for EPA to
address this issue, we will do so in the future via separate
guidance or rulemaking.
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The question of what is a natural versus an anthropogenic fire has
particular significance in considering the impacts of wildland fires on
air quality and how they should be regarded under today's proposed
rule. Federal land managers have given recognition to several different
types of wildland fires, depending on their causal circumstances and
the role that such fires play in the affected ecosystems. ``Wildfires''
are described as unplanned, unwanted wildland fires, and include
unauthorized burns (such as arson or acts of carelessness by campers),
prescribed burns that escape control due to unforeseen circumstances,
or other wildland fires where the primary objective is to suppress the
fire as quickly as possible.
In contrast, ``wildland fire use'' fires are those which were
ignited naturally or unintentionally (e.g., as the result of lightning)
and are allowed to continue burning without suppression efforts in
locations that have been designated in fire management plans as areas
where fires are necessary and desirable to accomplish specific resource
management objectives. ``Prescribed fires'' are those ignited purposely
to accomplish specific management objectives, and have been subject to
written, approved prescribed fire plans (``Interagency Strategy for
Directives Task Group,'' Memorandum from National Fire and Aviation
Executive Board to Agency Personnel: Bureau of Indian Affairs, Bureau
of Land Management, National Park Service, U.S. Fish and Wildlife
Service, USDA Forest Service, April 18, 2005). Under these
classifications, we believe that wildfires due to whatever causes them
clearly fall within the meaning of ``natural events'' as that term is
used in section 319. Similarly, we believe that wildland fire use fires
qualify as ``natural events'' by virtue of their natural origins.
Prescribed fires, however, cannot be classified as ``natural,''
given their clearly anthropogenic origins. Nonetheless, we believe that
prescribed fires are not automatically excluded from the definition of
exceptional events. If a prescribed fire meets the statutory criteria
of being ``unlikely to recur at the same location'' or ``not reasonably
controllable or preventable,'' and the measures specified below, it may
qualify as an exceptional event.
Prescribed fires carried out for resource management objectives are
frequently designed to restore the role of wildland fires as they once
occurred under natural conditions. As such, their expected frequency
can vary widely, depending on the fire regenerative cycle of a
particular landscape or wildland ecosystem. The natural fire cycle can
range from once every year to less frequently than once in 35-60 years.
Thus in many, though not all, cases it may be demonstrated that the
likelihood of recurrence is sufficiently small that these events should
be accorded special consideration under the rule.
Since a prescribed fire is being deliberately ignited, it does not
qualify as ``natural,'' and one view is that it cannot qualify as ``not
reasonably controllable or preventable.'' However, a different
interpretation of this provision of section 319 examines whether there
are any reasonable alternatives to the use of fire in light of the
needs and objectives to be served by it. For instance, there may be a
sufficient build-up of forest fuels in a particular area that if left
unaddressed would pose an unacceptable risk of catastrophic wildfire,
which result in adverse impacts of much greater magnitude and severity
than would result from the careful use of prescribed fires. A
particular ecosystem may also be highly dependent on a natural fire
cycle to maintain a sustainable natural species composition.
Alternatively, pest or disease outbreaks in an area may be such that
there are no reasonable alternatives to fire. In some cases, other
legal requirements may preclude the use of mechanical fuel reduction
methods such as in designated wilderness or National Parks. Where such
ecological conditions exist, or where mechanical or other treatments
are not reasonably feasible for reasons that include, but are not
limited to, a lack of access or severe topography, we believe that it
would be appropriate to exclude the impacts from well-managed
prescribed fires to address them. Well-managed prescribed fires are
those that consider smoke impacts prior to and during the burn, barring
unforeseen circumstances, and when the prescribed fire is in compliance
with a Smoke Management Plan (SMP).
The EPA is proposing in this action that States continue to follow
the smoke management provisions described in the ``Interim Air Quality
Policy on Wildland and Prescribed Fires,'' issued May 15, 1998
(Wildland and Prescribed Fire Policy). This policy provides that EPA
will allow exceedances to be discounted that have been flagged by a
State as having been caused by prescribed fires used for purposes of
resource management provided that the State certifies that it has
adopted and is implementing a certified SMP as described in our policy.
Under our proposal, if a State, local, or Tribal air quality agency
does not certify that a basic SMP is being implemented, or that basic
smoke management practices are being employed by burners, EPA would not
exclude data related to exceedances or violations attributed to
prescribed fires managed for resource benefits.
We request comments on the interpretation of prescribed fire
described above on the proposed requirements for SMPs, and on any
additional criteria or conditions that should be considered in
determining whether and under what circumstances prescribed fires
should be considered to be exceptional events.
e. Stratospheric Ozone Intrusions. Stratospheric ozone intrusion is
considered to be a natural event. A stratospheric ozone intrusion
occurs when a parcel of air originating in the stratosphere, which is
at an average height of 20 km or 12.4 miles, is re-entrained directly
to the surface of the earth. Stratospheric ozone intrusions are very
infrequent, localized events of short duration. They are typically
associated with strong frontal passages and, thus, may occur primarily
during the spring season.
IV. The Management of Air Quality Data Affected by Exceptional Events
The EPA is proposing that, in order to exclude air quality data
from consideration for regulatory purposes, States must follow the
procedures, timelines, and other requirements described in this
proposed rule. Specifically, States must clearly identify, or ``flag,''
data they believe to be influenced by such events; they must show that
they have flagged days on which air quality has been ``affected'' by
exceptional events according to EPA criteria; and they must submit
appropriate documentation demonstrating that the exceptional event
caused the exceedance or violation of the NAAQS in question. Each of
these steps is described in detail below.
[[Page 12598]]
A. Flagging of Data in the AQS Data Base
Air quality data are required, pursuant to 40 CFR part 58.35, to be
submitted to EPA by each State on a calendar quarterly basis, with
submissions due not later than 90 days after the end of a quarterly
reporting period. Once air quality data have been submitted to EPA, it
is possible to ``flag'' specific values for various purposes. ``Data
flagging'' refers to the act of making a notation in a designated field
of an electronic data record. The principal purpose of the data
flagging system in the AQS data base is to identify those air quality
measurements for which special attention or handling is warranted.
These include, but are not limited to, those measurements that are
influenced by exceptional events. In the case of exceptional events,
States place the initial flag on the data in the AQS data base.
Following an evaluation of the supporting documentation, EPA will
decide whether to concur with the flag; concurrence will be marked by
the placement of a second flag in the AQS data base by EPA. Once EPA
has concurred on the flag, the data will be excluded from regulatory
decisions such as determinations of attainment or nonattainment.
While the flagging of data by the State is the first step in an
exceptional events demonstration, it is insufficient by itself to allow
for the exclusion of data. In order to have EPA concur on a flag,
States must meet the additional requirements described below. As
explained, the State has the responsibility to document both the
occurrence of the event and the causal connection to the monitoring
data under consideration. Because the initial step of flagging the data
is a relatively simple one, States may flag many more days than the
number of days for which they ultimately submit documentation to
support exclusion.
B. What Does It Mean for an Event To ``Affect Air Quality''?
It is important to recognize that any emissions-producing event has
the potential to have some influence on downwind air quality. Indeed,
on any given day, measured air quality at any given location will
reflect the influences of a variety of activities, including both
natural and anthropogenic emissions from both local and remote upwind
sources. The EPA believes that it would be unreasonable to exclude data
affected by an exceptional event simply because of a trivial
contribution of the event to air quality. Furthermore, we also believe
that it would be unreasonable to exclude more significant, but routine
background air quality impacts, as this would disregard an important
part of the public's exposure to air pollution upon which EPA's air
quality standards are based. The effect of such exclusion would be an
inappropriate reduction in the stringency of the NAAQS, rather than
providing specific relief under the circumstances provided in section
319 for which States should not be designated nonattainment or be
required to prepare control strategies.
Neither section 319 nor its legislative history provides precise
guidance on what should be considered when determining whether an event
``affects air quality'' and thus qualifies to be considered for
exclusion or special treatment. However, section 319(b)(3)(B)(ii) and
(iv) provide that there must be a ``clear causal relationship'' between
a measured exceedance of a standard and the event to show that the
event ``caused a specific air pollution concentration;'' and it must be
shown that the data in question are ``directly due'' to an exceptional
event. Moreover, one of the principles provided by section 319(b)(3)(A)
indicate that the protection of public health is the highest priority.
For these reasons, we are proposing that for an event to qualify as
``exceptional'' for purposes of special regulatory consideration, its
air quality impact must fall both above the level of the applicable
standard (i.e., must be an ``exceedance'' as required by section 319)
and significantly beyond the normal fluctuating range of air quality,
including background air quality concentrations, and should be large
enough so that without it there would have been no exceedance. We next
provide several alternative approaches to determining whether and when
air quality is ``affected by'' exceptional events, and request comment
on which of these approaches is most suitable for demonstrating such
impacts.
1. Option 1: 95th Percentile Criterion
The first proposed approach is essentially a test for statistical
deviations from the norm. For measurement days on which the event can
be shown to have an air quality impact, the measurement would be
compared to the 95th percentile of measurements typical of days in the
particular calendar quarter that are not influenced by exceptional
events (``non-event days''). The typical days could be based on a 3-5
year period of record which exclude days influenced by exceptional
events. Under this option, only an event whose resulting concentrations
meet or exceed the 95th percentile criterion, along with meeting the
other criteria in this proposed rule would qualify for exclusion from
regulatory consideration.
In evaluating available air quality data, we have found that by
limiting consideration to those concentrations above the 95th
percentile, only those concentrations that fall approximately two
standard deviations above the mean of concentrations for that quarter
would generally be excluded (See memo from Mark Schmidt, OAQPS, to
docket entitled ``Analysis of Flagged Particulate Matter Data,''
February 10, 2006). Excluding days on which concentrations caused by
exceptional events exceed the 95th percentile threshold employs a
general test of statistical significance and has the effect of ensuring
that such concentrations would clearly fall beyond the range of normal
expectations for air quality during a particular time of year.
In our analysis of flagged and excluded air quality data for the
period 1999-2004, we found that application of the 95th percentile
criterion would result in the exclusion of approximately 85 percent of
data previously flagged by States and concurred on by EPA. Thus, this
approach would result in a somewhat more rigorous qualification
requirement than is reflected in EPA's past case-by-case approach.
Previously, EPA did not have a concentration threshold or other
quantitative criteria to determine which days would be eligible for
exclusion due to exceptional events. As indicated above, approximately
15 percent of the flags that were concurred on were concentrations that
were not necessarily statistically distinguishable from routine levels.
The 95th percentile approach could also help to eliminate some of the
variability from State to State and Region to Region: as described in
Schmidt (2006), rates of flagging and the severity of pollution on
flagged days have varied significantly among States and regions in the
past. For PM2.5, for example, many States flagged no days
between 1999-2004, while Puerto Rico flagged 15 percent of all of its
PM2.5 data. Also, while most PM2.5 flags during
this period were above the 95th percentile, some States flagged data at
the 75th percentile or lower. (See memo from Mark Schmidt, OAQPS, to
docket entitled ``Analysis of Flagged Particulate Matter Data,''
February 10, 2006.)
2. Option 2: 75th Percentile/95th Percentile Tiered Approach
Under this approach, we propose to retain flexibility to determine
whether concentrations less than the 95th percentile but above the norm
should
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qualify for exclusion as ``affecting air quality.'' In particular,
multiple measurement values over time with relatively small individual
event impacts may collectively affect an annual average concentration
to a significant degree. States may wish to consider whether to exclude
such impacts if the average concentration is close to the level of the
annual NAAQS. Therefore, we are soliciting comment on a second approach
whereby measured values are compared both to the historical 95th
percentile of non-event days and to the 75th percentile of such days.
Where concentrations caused by an exceptional event meet or exceed
the 95th percentile criterion, they would be conclusively determined to
qualify for exclusion subject to the other requirements of this
proposed rule. Where concentrations caused by an exceptional event do
not meet the 95th percentile criterion, we would provide a further
opportunity for States to make demonstrations which satisfy the other
criteria in this proposed rule, so long as values exceeded the 75th
percentile of non-event days. This approach would provide for a more
flexible approach and would rely on a weight-of-evidence demonstration
that would permit States to make other sorts of showings that the
concentrations caused by the event were in some way unusual or not
representative of normal air quality and thus should not result in
additional regulatory requirements.
When we applied the 75 percent percentile criterion to our analysis
of flagged and excluded air quality data for the period 1999-2004, we
found that this criterion would make nearly all of the data previously
flagged by States and concurred on by EPA eligible for exclusion. Thus,
we expect this approach would have a result that is roughly consistent
with EPA's past case-by-case approach.
3. Option 3: Case-by-Case Approach Based on Weight of Evidence
The third option is to permit the more general case-by-case
evaluation, without threshold criteria, that may be guided by the
magnitude of the measured concentration on days affected by exceptional
events relative to historical, seasonally adjusted air quality levels.
This approach is most nearly analogous to our historical treatment of
exceptional events but, in contrast to Options 1 and 2, provides the
least definitive guidance to assist States in their evaluations.
Nevertheless, the case-by-case approach allows for consideration of
days with ambient concentrations which are not necessarily among the
highest concentrations that have been historically observed. In fact,
25 percent of days have concentrations greater than the median value
but less than the 75th percentile. While such days are unlikely to
impact short-term standards, discounting such days can certainly have
an impact on an annual average concentration. In general, however,
demonstration that an event caused a concentration which is essentially
indistinguishable from routine air quality would be very difficult to
document, and this approach may make it difficult for EPA regions to be
consistent when determining whether to concur on a flag.
We request comment on which of these proposed options should be
included in the final rule, including the appropriateness of proposed
statistical criteria, the period of record on which to base the 95th
and 75th percentile and conclusions about normal air quality
expectations (e.g., 3 years, 5 years, or some longer period of record),
and any other criteria or procedures we should consider adopting along
with one of these options.
C. Use of a ``But For'' Test
There may be instances in which exceptional events may have a
significant impact on air quality on days when concentrations are
already above the applicable standard in the absence of the influence
of such events. In such cases, it is important to preserve and consider
all valid air quality data influenced by activities which properly fall
within the responsibilities of States to manage for purposes of air
quality attainment and maintenance. For this reason, we are proposing
to require that air quality data may not be excluded except where
States show that exceedances or violations of applicable standards
would not have occurred ``but for'' the influence of exceptional
events. In other words, to the extent it is possible to determine that
the resulting air quality concentrations and appropriate design values
for an area would be above the level of the standards even without the
influence of the exceptional event, the air quality data for the day(s)
in question should not be excluded. However, consideration of the
impacts of exceptional events on air quality values for control
strategy planning purposes may be appropriate, and States are
encouraged to consult with the appropriate EPA regional offices to
further discuss this issue.
D. Schedules and Procedures for Flagging and Requesting Exclusion of
Data
In establishing procedures and timetables for States to request,
and EPA to grant, exclusion of data affected by exceptional events, we
are guided by two competing considerations: ensuring States have
adequate time and opportunity to compile and evaluate all relevant and
available information in support of such requests; and making
determinations in a timely manner so that all pertinent and valid air
quality data would be appropriately considered in regulatory
determinations. To assist EPA in determining the best approach to
managing the data flagging process and submissions of demonstrations
for the final rule, we are proposing three alternatives for public
review and comment.
1. Option 1: Early Data Flagging and Demonstration Submission
The first approach would establish a two-step process for
identification of data and submission of demonstrations. This process
provides for the early flagging of data and the notification of the
appropriate EPA Regional Office concerning the State's intention to
seek exclusion of data, followed by a longer timeframe for States to
prepare and submit their demonstrations.
Under this approach, we would require a State to flag the data that
they believe to be affected by exceptional events at the time of
submission of the air quality data to EPA's AQS data base, in
accordance with the schedule described in 40 CFR part 50.35, which is
generally no later than 90 days after the end of the calendar quarter.
This approach would ensure that the flagging process remains consistent
with the timeline set forth in rules governing data submission
requirements.
Just as the scope and substance of demonstrations in support of
requests for exclusion will vary depending on facts and circumstances
(see section IV.F. below), so, too, will the time required for such
demonstrations. Where air quality in an area is influenced by a
relatively small set of emission sources with well-defined emission
profiles and limited pollutant species, a demonstration that an air
quality measurement influenced by a particular event merits exclusion
may be relatively simple to make. In other cases, such as where the
number and types of sources contributing to measured air quality
concentrations are extremely complex and varied, making it more
difficult to distinguish between the effects of routine activities and
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unusual ones, more time and effort will be needed for a State to
provide an adequate demonstration in support of its request.
For these reasons, we are proposing under this option to require
States to notify the appropriate EPA Regional Office of their intent to
seek exclusion of data due to exceptional events at the time of
submission of quarterly air quality data to the AQS data base. We are
also proposing to require the State to consult with the EPA Regional
Office as soon as reasonably possible after notification about the
event, its suspected air quality impact, and the demonstration needed
to justify a decision to exclude the data from regulatory
consideration. This is intended to enable the State and EPA to work
together during the process of data analysis and documentation to
ensure that a complete and well-supported demonstration is submitted in
a timely manner.
With respect to demonstrations in support of requests for exclusion
of data, we are proposing under this option to provide States with more
time to submit the necessary demonstration. We propose that States
submit complete demonstrations to EPA not later than 180 days following
the close of the quarter in which the event occurred. Based on past
experience with exceptional events and associated data analyses, we
believe that this will provide adequate time in most cases for States
to identify, compile, and evaluate all relevant factors pertaining to
an exceptional event and its impacts. However, in special circumstances
where additional time is required to make a complete submission, and
where the outcome of such additional efforts is likely to have a
substantial impact on the demonstration, we are proposing to allow
States to request extensions of up to 90 additional days. We expect
that such extensions under this option would be the exception, rather
than the rule, and that they will be limited to special circumstances
necessitating more complex and sophisticated analyses, such as where
the collection and analysis of species-specific data in urban areas may
be needed in order to characterize and quantify an event's contribution
to air quality at a particular location. Under this option, as well as
the options addressed below, once EPA receives a State's demonstration,
EPA will then have a 30-day period to review the demonstration and
provide a concurrence or nonconcurrence on the flag in the AQS data
base. The EPA expects that, in most cases, a period of 30 days will be
enough time to review and provide a concurrence related to a State's
request to exclude data affected by an exceptional event. However, for
more complex demonstrations, EPA may require more time for its review.
In such cases, EPA may extend the time for its review by not more than
an additional 30 days.
2. Option 2: Early Data Flagging and Delayed Demonstration Submission
Under this option, we are proposing the same requirements for the
flagging of data and notification of the appropriate EPA Regional
Office as described in Option 1. However, under Option 2, we propose to
allow up to