Treatment of Data Influenced by Exceptional Events, 13560-13581 [E7-5156]
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13560
Federal Register / Vol. 72, No. 55 / Thursday, March 22, 2007 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 50 and 51
[EPA–HQ–OAR–2005–0159; FRL–8289–5]
RIN 2060–AN40
Treatment of Data Influenced by
Exceptional Events
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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AGENCY:
SUMMARY: This action finalizes 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 finalizing the proposal 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. The EPA is also requiring
States to take reasonable measures to
mitigate the impacts of an exceptional
event.
DATES: This final rule is effective May
21, 2007.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2005–0159. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information is not publicly available,
i.e., confidential business information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
https://www.regulations.gov or in hard
copy at the OAR Docket, EPA/DC, EPA
West, Room 3334, 1301 Constitution
Ave., NW., Washington, DC. The Public
Reading Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Air and Radiation
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Docket and Information Center is (202)
566–1742.
FOR FURTHER INFORMATION CONTACT:
General questions regarding the final
rule should be addressed to Mr. Larry D.
Wallace, PhD, 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 final rule
should be addressed to Mr. Neil Frank,
Office of Air Quality Planning and
Standards, Air Quality Assessment
Division, Mail Code C304–01, Research
Triangle Park, NC 27711; telephone
(919) 541–5560, and e-mail address
frank.neil@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
Regulated Entities. This final rule will
affect State and local air quality
agencies. This rule may also affect
Tribal air quality agencies that have
implemented air quality monitoring
networks or have authority to
implement air quality programs.
This list is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by this action. This list gives
examples of the types of entities EPA is
now aware could potentially be
regulated by this action. Other types of
entities not listed could also be affected.
To determine whether your facility,
company, business, organization, etc., is
regulated by this action, you should
examine the applicability criteria in
section IV of this preamble. If you have
any questions regarding the
applicability of this action to a
particular entity, consult the people
listed in the preceding section.
B. How Is This Preamble Organized?
Table of Contents
The following is an outline of the
preamble.
I. General Information
A. Does This Action Apply to Me?
B. How Is This Preamble Organized?
II. Preamble Glossary of Terms and
Acronyms
III. Background and Purpose of This
Rulemaking
A. Legislative Requirements
B. Historical Experience Concerning
Exceptional and Natural Events
IV. This Final Action
A. To Whom and to What Pollutants Does
This Rule Apply?
B. How Does This Rule Relate to Indian
Tribes?
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C. Comments Submitted on the Proposed
Rule
D. What Is an Exceptional Event?
E. 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. Natural Disasters and Associated CleanUp Activities
b. Volcanic and Seismic Activities
c. High Wind Events
d. Wildland Fires
e. Stratospheric Ozone Intrusions
6. Prescribed Fire
V. The Management of Air Quality Data
Affected by Exceptional Events
A. Flagging of Data in the AQS Database
1. Background
2. Final Rule
3. Comments and Responses
B. What Does It Mean for an Event to
‘‘Affect Air Quality’’?
1. Background
2. Final Rule
3. Comments and Responses
C. Use of a ‘‘But For’’ Test
1. Background
2. Final Rule
3. Comments and Responses
D. Schedules and Procedures for Flagging
and Requesting Exclusion of Data
1. Background
2. Final Rule
3. Comments and Responses
E. Exclusion of Entire 24-Hour Value as
Opposed to a Partial Adjustment of the
24-Hour Value
1. Background
2. Final Rule
3. Comments and Responses
F. What Should States Be Required To
Submit in Their Exceptional Events
Demonstrations?
1. Background
2. Final Rule
3. Comments and Responses
G. Public Availability of Air Quality Data
and Demonstrations Related to
Exceptional Events
1. Background
2. Final Rule
3. Comments and Responses
VI. Additional Requirements
A. Requirements for States To Provide
Public Notification, Public Education,
and Appropriate and Reasonable
Measures To Protect Public Health
1. Background
2. Final Rule
3. Comments and Responses
VII. Special Treatment of Certain Exceptional
Events Under This Final Rule
A. Volcanic and Seismic Activities
1. Background
2. Final Rule
B. High Wind Events
1. Background
2. Final Rule
C. Stratospheric Ozone Intrusion
1. Background
2. Final Rule
VIII. Treatment of Fireworks Displays
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A. Background
B. Final Rule
C. Comments and Responses
IX. 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
J. Congressional Review Act
K. Petitions for Judicial Review
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II. Preamble Glossary of Terms and
Acronyms
The following are abbreviations of
terms used in the preamble.
ARM Approved Regional Methods.
AQS Air Quality System.
BACM Best Available Control
Measures.
CAA Clean Air Act.
CAAA Clean Air Act Amendments.
EPA Environmental Protection
Agency.
FEM Federal Equivalent Methods.
FIP Federal Implementation Plan.
FR Federal Register.
FRM Federal Reference Methods.
NAAQS National Ambient Air Quality
Standards.
NEAP Natural Events Action Plan.
NEPA National Environmental Policy
Act.
NTTA National Technology Transfer
Advancement Act of 1995.
OAQPS Office of Air Quality Planning
and Standards.
OMB Office of Management and
Budget.
PM Particulate matter.
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 Program.
TAR Tribal Authority Rule.
TIP Tribal Implementation Plan.
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UMRA Unfunded Mandates Reform
Act.
USDA U.S. Department of Agriculture.
VCS Voluntary Consensus Standards.
III. Background and Purpose of This
Rulemaking
A. Legislative Requirements
We 1 are finalizing 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,
required EPA to publish the proposed
rule in the Federal Register no later
than March 1, 2006.2 Further, EPA must
issue this final rule no later than 1 year
from the date of proposal. The EPA
published the proposed rule on March
10, 2006 (See 71 FR 12592).
In this final rule, EPA is establishing
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 an event that is not
reasonably controllable or preventable;
is an event caused by human activity
that is unlikely to recur at a particular
location or a natural event; and is
determined by EPA 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
temperatures 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.3 Section 319(b)(3)(B)(ii)
requires that ‘‘a clear causal
1 The
U.S. Environmental Protection Agency.
subsequent references to section 319 of the
CAA in this proposal are to section 319 as amended
by SAFE–TEA–LU unless otherwise noted.
3 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.
2 All
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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
exceedances or violations of the
NAAQS.
The term exceedance refers to a
measured or modeled concentration
greater than the level of one or more for
a pollutant. The NAAQS are also set
with particular averaging periods (e.g., 3
years for ozone and PM2.5) such that a
violation of the NAAQS for ozone and
PM2.5 requires an average annual
concentration level specified by
appendix I and N to 40 CFR 50 to be
greater than the level of the NAAQS.
Public comments favored the
consideration of data contributing to
both exceedances and violations for data
exclusion under this Rule. As discussed
in section V.C, exceedances of any
NAAQS will be eligible for
consideration for data exclusion and
any data contributing to violations of
daily or sub-daily standards will also be
eligible for consideration (e.g. 8-hour or
24-hour standards). Data contributing to
annual violations without being
exceedances themselves are considered
too close to background air quality
levels for exclusion under this Rule.
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 database 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,
Congress sought to provide statutory
relief to States to allow them to avoid
being designated as nonattainment or to
avoid continuing to be designated
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nonattainment as a result of exceptional
events in appropriate circumstances. 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.
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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,
‘‘Guideline for the Interpretation of Air
Quality Standards,’’ Guideline No. 1.2–
008 (revised February 1977).4
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.5 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 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
4 ‘‘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.
5 Federal Register (52 FR 24667), July 1, 1987.
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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 are 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).6
On July 18, 1997, EPA issued a
revised NAAQS for ozone and a new
NAAQS addressing PM2.5. For ozone,
the revised NAAQS provided for an 8hour 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 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, related to the ozone
standard, addresses the treatment of
data determined to be influenced
natural events, and section 1.0(b) of
appendix N, related to the PM2.5
standard, provides that EPA may give
special consideration to data
determined to be affected by an
exceptional or natural event.
Appendices K, I, and N, which are
parts 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) database for use
in making regulatory decisions, in some
cases it may be appropriate for EPA 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-bycase 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
6 Memorandum from Mary D. Nicols, Assistant
Administrator for Air and Radiation, to EPA
Regional Offices entitled, ‘‘Areas Affected by PM10
Natural Events,’’ May 30, 1996.
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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.7 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.8
IV. This Final Action
A. To Whom and to What Pollutants
Does This 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
database. 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
7 ‘‘Guideline on Data Handling Conventions for
the PM NAAQS,’’ United States Environmental
Protection Agency, Office of Air Quality Planning
and Standards, Research Triangle Park, NC 27711,
EPA–454/R–98–017, December 1998.
8 Following the promulgation of this rule, it is
EPA’s intention to begin the process to revise the
‘‘Interim Air Quality Policy on Wildland and
Prescribed Fires’’ in calendar year 2007 to update
the policy and to ensure that the policy is
consistent with this final rulemaking action. In
addition, it is EPA’s intent that agricultural
prescribed burning will be addressed when this
policy is updated and will also address basic smoke
management practices.
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responsible for reviewing and approving
or disapproving any requests for such
consideration. Therefore, this final rule
applies 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 rule
governs 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 rule would govern those actions as
well.
At present, only the NAAQS for ozone
and particulate matter (PM) contain
provisions which allow for the special
handling of air quality data affected by
exceptional and natural 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 only applying the
provisions of this rule initially to ozone
and PM.9 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 provisions 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
9 Section IV.G of the preamble to the Proposed
Rule discussed special considerations relevant to a
new NAAQS for PM10–2.5 proposed by EPA on
December 20, 2005. This proposed standard would
have drawn a distinction between coarse particles
of urban versus non-urban origin, which raised new
issues about the handling of exceedances of the
coarse particle standard caused by exceptional
events. However, in EPA’s final rule on the PM
NAAQS, issued September 21, 2006, EPA retained
the existing 24-hour PM10 standard instead of
promulgating the proposed PM10–2.5 standard. Thus,
section IV.G of the preamble to the Proposed Rule
is no longer relevant and has been removed from
this Preamble.
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107(d)(3) not to redesignate affected
areas as nonattainment based on these
events. We also intend to use our
discretion under this rule to address
determinations for the ozone standard
related to the treatment of data
influenced by both exceptional and
natural events. Currently, appendix I,
only addresses the treatment of data
determined to be influenced by a
stratospheric ozone intrusion and other
natural events, but does not address the
handling of data influenced by other
exceptional 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).
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 final 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 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 rule). The EPA
intends to work with Tribes on the
implementation of this 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 rule.
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C. Comments Submitted on the
Proposed Rule
The proposed rule on the ‘‘Treatment
of Data Influenced by Exceptional
Events’’ was issued on March 10, 2006
(71 FR 12592). We received 98 letters
from commenters representing 587
comments from private citizens, State
and local governments, industry,
environmental groups, and Federal
agencies. Sections V, VI, VII, and VIII of
this notice describe the primary
elements and requirements concerning
the process for the handling of data
influenced by exceptional events. Each
section summarizes the relevant issues
and options discussed in the proposed
rule and provides the final decisions
related to the issues for each section. In
this preamble, we have provided
responses to certain significant
comments to elaborate or provide
clarification for EPA’s decision on an
issue discussed in the relevant section
of the rule. We have developed a
response to comments document which
addresses all of the timely comments
received on the proposed rule.
Following the promulgation of this rule,
the response to comments document
will be placed into the docket of this
rulemaking action for public review
(See Docket No. EPA–HQ–OAR–2005–
0159).
D. What Is an Exceptional Event?
In accordance with the language in
section 319, EPA is defining 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 EPA 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
the purposes of this rule, EPA is
defining ‘‘natural event’’ as an event in
which human activity plays little or no
direct causal role 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
adopting section 188(f) of part D,
subpart 4, of the 1990 amendments to
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the CAA, Congress recognized and
provided for distinctions between these
types of events with respect to waiver of
applicable requirements and the
extension of otherwise applicable
attainment dates for the PM10 standard.
In approving section 188(f) of the CAA,
the House committee of jurisdiction
discussed a circumstance in which
recurring emissions from a source
should be considered to be
anthropogenic. The House report noted
EPA statements that, in the cited case,
high concentrations of dust from a
lakebed were due to human activity, i.e.,
the long-term diversion of water from a
lake. (See Pub. L. 101–549, CAA
Amendments of 1990 House Report No.
101–290(l), May 17, 1990; and
discussion of Mono Lake, California
therein). Also, EPA recognized, in
recently acting to retain PM10 as a
measure of coarse particulate, that in
some instances exceedances of this
NAAQS ‘‘may be caused in whole or in
part, by exceptional events, including
natural events such as windstorms
* * *. (and that) an exceedance may be
treated as an exceptional event even
though anthropogenic sources such as
agricultural and mining emissions
contribute to the exceedance.’’ (71 FR
61216; October 17, 2006).
In this final 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 finalizing 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.
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E. 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 rule provided that
all other requirements of the rule are
met. By providing the examples listed
below, EPA is not determining that such
events are the only types of events that
may qualify for exclusion under the rule
as exceptional events. Other events that
meet the statutory criteria for an
exceptional event as defined in this rule
may also qualify for exclusion. The AQS
user documentation contains a list of
other similar events that may be flagged
for special consideration. (https://
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www.epa.gov/ttn/airs/airsaqs/manuals/
qualifiers.htm).10
In addition, in the sections below, we
have provided responses to certain
significant comments received during
the comment period for the proposed
rule regarding the examples of events
that may meet the definition of an
exceptional event in order to elaborate
upon or provide clarification about what
constitutes an exceptional event.
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.
Comments and Responses
Comment: Several commenters stated
that ‘‘Chemical Spills and Industrial
Accidents’’ should generally not be
considered exceptional events.
Commenters stated that most industrial
accidents and chemical spills are
reasonably controllable and preventable
with proper planning and mitigation
efforts. These commenters stated that
allowing for accidents or spills that
could have been avoided is inconsistent
with the CAA.
Response: It is EPA’s belief that air
quality data that has been affected by
emissions from chemical spills,
industrial accidents, or structural fires
may be flagged by a State as an
exceptional event and reviewed by EPA
for exclusion on a case-by-case basis to
determine whether it meets the criteria
for exceptional events as defined in this
rule. In particular, data influenced by
chemical spills or industrial accidents
must be demonstrated to have ‘‘affected
air quality’’ and must be demonstrated
to be due to circumstances that were not
reasonably controllable or preventable
and are events that are unlikely to recur
in a particular location. The EPA agrees
with the commenters that industrial or
point source emissions due to
malfunctions or non-compliance would
not be considered exceptional events
and should be addressed through the
normal State Implementation Planning
process.
2. Structural Fires
Structural fires include any accidental
fire involving a manmade structure.
Comments and Responses
Comment: Several commenters
indicated that ‘‘Structural Fires’’ should
10 The EPA will be revising the list of events
contained in the AQS database following the
promulgation of this rule to ensure that the list is
consistent with the requirements of the rule.
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generally not be considered exceptional
events. Commenters stated that these
types of events should be considered as
emissions from anthropogenic sources
and handled within the form of the
respective air quality standards where a
certain number of exceedances of the
standards are allowed over a 3-year
period. Commenters assert that
structural fires, lasting for several hours,
are unlikely to cause an area to reach
the level of nonattainment. In cases
where structural fires are determined to
be the cause of a monitored violation of
the NAAQS, commenters stated that
EPA should adopt a case-by-case review
of these events.
Response: The definition of structural
fires under this rule pertains to any
accidental fire involving a manmade
structure. The EPA believes that
structural fires could be an exceptional
event under this rule, provided all other
requirements of the rule are met,
because they could ‘‘affect air quality,’’
could be an event that is not
‘‘reasonably controllable’’ or
‘‘preventable,’’ and could be events that
are caused by human activity that are
unlikely to recur at the same location.
However, EPA agrees with the
commenters that these types of events,
as well as other similar types of events,
should be reviewed on a case-by-case
basis to determine whether they meet
the criteria for an exceptional event as
defined by this rule.
3. Exceedances Due to Transported
Pollution
Transported pollution, whether
national or international in origin, and
whether from natural or anthropogenic
sources, may cause exceedances eligible
for exclusion under this rule, as long as
all of the criteria and requirements
related to exceptional events are met as
defined in this rule. 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 in
an area, leading to exceedances or
violations of a NAAQS. An example of
interstate transported emissions which
may be flagged as due to an exceptional
event would be emissions due to smoke
from wildfires or wildland fire use fires
which cause exceedances or violations
of the NAAQS at monitoring sites in
other States. Other examples could
include data affected by emissions from
mining and agricultural activities when
such emissions are subjected to longrange transport, and the criteria and
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requirements related to an exceptional
event are met as defined in this rule. In
general, events due to transported
pollution may be considered on a caseby-case basis.
Comments and Responses
Comment: Several commenters
expressed concern over EPA allowing
the exceptional events rule to be used to
exclude data that has been affected by
emissions emanating from sources
outside the borders of the United States.
Response: States may flag data that
has been affected by sources emanating
from outside the United States that meet
the criteria for an exceptional event as
defined under this rule, including
requirements for causation and
documentation. In cases where an area
is impacted by emissions from sources
outside of the United States which do
not meet the criteria for an exceptional
event under this rule, and these
emissions contribute to an area being
designated as nonattainment, the
emissions may be addressed under
section 179B of the CAA related to
‘‘International Border Areas.’’ Section
179B provides that where a State is
required to submit a State
Implementation Plan (SIP) to address
issues related to a nonattainment
designation, EPA may approve the SIP
for the area provided that the plan (1)
meets all the applicable requirements
called for under the CAA, other than the
requirement that the plan demonstrate
attainment or maintenance of the
NAAQS, and (2) the SIP must
demonstrate that the affected area
would be able to attain the standard by
the applicable attainment date ‘‘but for’’
emissions emanating from outside the
United States.
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.
Comments and Responses
No comments were received on this
topic.
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5. Natural Events
The natural events addressed by this
final rule are: (1) Natural disasters and
associated cleanup activities; (2)
volcanic and seismic activities; (3) high
wind events; (4) wildfires and wildland
fire use fires; and (5) stratospheric ozone
intrusions. The EPA will consider other
types of natural events on a case-by-case
basis.
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a. Natural Disasters and Associated
Clean-Up Activities
For the purpose of flagging, major
natural disasters such as hurricanes and
tornadoes for which State, local, or
Federal relief has been granted, and
clean-up activities associated with these
events, may be considered exceptional
events. The EPA believes that for a
major natural disaster, a timeframe up to
12 months is a reasonable time period
to allow for clean-up activities
associated with these types of activities.
In cases where the damage caused by
the event is so substantial that a 12month period is inadequate to address
the clean up that is necessary, a State
may submit a request to EPA for an
extension of the 12-month time period.
The EPA will grant requests for
extensions of the time period related to
such events on a case-by-case basis if
the States submit adequate supporting
information concerning the reason for
the extension as well as the length of
time being requested for the extension.
Comments and Responses
Comment: Several commenters
indicated that EPA should limit the time
period associated with clean-up
activities due to a natural disaster. One
commenter indicated that the
exceptional events rule as proposed
would allow States to apply the term
‘‘natural disaster’’ very broadly to
include circumstances that would
circumvent the intent of the CAA. For
example, declaring an episode of high
summer temperatures to be a natural
disaster could potentially allow a State
to exclude high ozone levels which
commonly occur during hot weather.
Response: A time period up to 12
months for clean-up activities is
permitted for major natural disasters,
such as hurricanes and tornadoes, for
which State, local, or Federal relief has
been granted, may be flagged for
exclusion as exceptional events under
this rule. The clean-up activities
associated with these types of events
may also be flagged for exclusion as
being due to an exceptional event.
Given the nature of a major natural
disaster, the 12-month time period
allowed for clean-up activities following
such disaster is a reasonable time
period, and is consistent with the time
period being allowed for volcanic and
seismic activities under this rule. The
period of high summer temperatures
noted in the comment would not
represent a major natural disaster, as
described above, subject to the 12month clean-up period.
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b. Volcanic and Seismic Activities
Ambient concentrations of particulate
matter for which volcanic or seismic
activity caused or significantly
contributed to high levels of particulate
matter in an affected area will be treated
as natural events. While generally 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 activities can
contribute to ambient concentrations in
several ways: it may influence
concentrations of particulate matter 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 which may lead
to exceedances or violations of the
NAAQS.
Comments and Responses
Comment: Several commenters
indicated that the rule should provide
sufficient flexibility for data to be
excluded where the duration of the
event may last for a long period of time.
An example of such an event is where
volcanic activities last for several days.
Response: The EPA agrees with the
commenters and notes that the rule
allows for States to flag data and submit
documentation related to events such as
long-term volcanic and seismic
activities. States may also submit
requests to EPA to extend the time
period up to 12 months for major
natural disasters, for clean-up activities
following volcanic and seismic events.
States are encouraged to submit
supporting information related to the
reasons for the requested extension and
the length of time being requested for
the extension.
c. High Wind Events
High wind events are events that
affect ambient particulate matter
concentrations through the raising of
dust or through the re-entrainment of
material that has been deposited. In
some locations, concentrations of coarse
particles like PM10 are most likely
affected by these types of events,
although PM2.5 standards may be
exceeded under such circumstances as
well. Section VII.B. also includes a
discussion of this issue.
Comments and Responses
Comment: Several commenters
suggested that EPA replace the term
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‘‘high winds’’ with the term ‘‘windgenerated dust’’ because (1) it places the
emphasis on the natural mechanism, (2)
dust may become entrained at relatively
low wind velocities, and (3) the change
will eliminate confusion between the
wind speeds associated with a natural
event and wind speeds needed to
qualify for a ‘‘high wind’’ exceptional
event under EPA’s 1986 guidance.
Response: The EPA is retaining the
term ‘‘high wind’’ event because it
accurately connotes the type of natural
event that should be excluded under
this rule, as well as the action which
caused the exceedance or violation of
the standard. The term also serves as an
indicator concerning the level of wind
which caused the exceedance or
violation of the standard and indicates
that it was unusually high for the
affected area during the time period that
the event occurred. Therefore, States
must provide appropriate
documentation to substantiate why the
level of wind speed associated with the
event in question should be considered
unusual for the affected area during the
time of year that the event occurred. The
EPA will evaluate such instances on a
case-by-case basis, including factors
such as historically typical windspeed
levels for the season of the year that the
event is claimed.11
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d. Wildland Fires
Federal land managers have afforded
recognition to several different types of
wildland fires (i.e., wildfire, wildland
fire use fire and prescribed fire),
depending on their causal
circumstances and the role that such
fires play in the affected ecosystems.
Prescribed fire is addressed more fully
in the following section.
The question of what is a natural
versus an anthropogenic fire has
particular significance when
considering the impacts of wildland
fires (wildfire, wildland fire use fire and
prescribed fire) on air quality and how
these impacts should be regarded under
this rule. A ‘‘wildfire’’ is defined as an
unplanned, unwanted wildland fire
11 As described elsewhere in the preamble, EPA
is adopting a weight of evidence approach to
demonstrate that an exceptional event caused an
exceedance or violation. Therefore, in instances
where the level of the wind speed results in
exceedances or violations of particulate matter, for
data affected by these events to be considered for
exclusion under the weight of evidence approach,
a clear causal relationship must be demonstrated
between the exceedances measured at the air
quality monitoring site and the high wind event in
question. EPA will consider in the weight of
evidence analysis winds that produce emissions
contributed to by anthropogenic activities that have
been controlled to the extent possible through use
of all reasonably available reasonable and
appropriate measures.
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(such as a fire caused by lightning), and
include unauthorized human-caused
fires (such as arson or acts of
carelessness by campers), escaped
prescribed fire projects (escaped control
due to unforeseen circumstances),
where the appropriate management
response includes the objective to
suppress the fire. In contrast, a
‘‘wildland fire use’’ fire is the
application of the appropriate
management response to a naturallyignited (e.g., as the result of lightning)
wildland fire to accomplish specific
resource management objectives in
predefined and designated areas where
fire is necessary and outlined in fire
management or land management plans.
Using these definitions, we believe
that both wildfires and wildland fire use
fires fall within the meaning of ‘‘natural
events’’ as that term is used in section
319. Therefore, ambient particulate
matter and ozone concentrations due to
smoke from a wildland fire will be
considered for treatment as an
exceptional event if the fire is
determined to be either a wildfire or
wildland fire use fire.
overall Fire Strategy after promulgation
of this rule.
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
transported 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.
Comments and Responses
Comments and Responses
Comment: One commenter stated that
EPA should update its approach to
stratospheric events, establish criteria
by which such events may be
determined, and credit States for the
impact of intrusion events on noncompliant ozone monitor readings.
Response: Stratospheric ozone
intrusion is identified as a natural event
under 40 CFR part 50, appendix I, for
ozone, and will be considered for
treatment as an exceptional event.
Comment: In general, commenters
strongly supported exempting wildfires
as exceptional events under the rule.
Response: The EPA acknowledges
support for the proposal to classify
wildfires as a potential exceptional
event. As noted above, the Agency states
that wildland fires will be excluded as
exceptional events if they meet the
criteria and requirements of the
exceptional events rule.
Comment: The Agency received
comments both supporting and
opposing the proposal allowing
wildland fire use fires to qualify as an
exceptional event.
Response: After reviewing Congress’
revisions to section 319, the various
Agency policies cited in the proposal,
and comments received, the Agency has
determined that wildland fire use fires
may also qualify as an exceptional
event. However, these types of fires
must also meet certain criteria. For
example, these fires must occur on
lands that have been designated in fire
management or land management plans
as areas where fires are necessary and
desirable to accomplish specific
resource management objectives.
Comment: Many commenters
supported EPA’s commitment to update
the 1998 Interim Air Quality Policy on
Wildland and Prescribed Fires to be
consistent with this rule.
Response: The Agency plans to begin
revising this policy in 2007 as part of its
6. Prescribed Fire
A ‘‘prescribed fire’’ is defined as any
fire ignited by management actions to
meet specific resource management
objectives. According to existing Federal
policy, prior to ignition a prescribed fire
must have an approved prescribed fire
plan and must meet the National
Environmental Policy Act (NEPA)
requirements (where applicable)(see
National Wildland Fire Coordination
Group Glossary of Wildland Fire
Terminology, 2003). For purposes of
section 319, a prescribed fire cannot be
classified as ‘‘natural,’’ given the extent
of the direct human causal connection,
however, a prescribed fire may meet the
statutory criteria defined in section 319
of ‘‘affect[ing] air quality,’’ being
‘‘unlikely to recur at a particular
location’’ and is ‘‘not reasonably
controllable or preventable.’’ The
determination of whether a prescribed
fire can be considered an exceptional
event should be made on a case-by-case
basis taking into account the factors
described below.
A prescribed fire carried out for
resource management objectives is
frequently designed to restore essential
ecological processes of fire and mimic
fire under natural conditions. As such,
a prescribed fire’s expected frequency
can vary widely, depending on the
natural fire return interval of a
particular landscape or wildland
ecosystem. The natural fire return
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interval can range from once every year
to less frequently than once in more
than 200 years. Thus, in many, though
not all cases, it may be possible to
demonstrate that the likelihood of
recurrence is sufficiently small enough
to show that a prescribed fire under
these conditions meets the ‘‘unlikely to
recur at a particular location’’
requirement of the statutory language.
A prescribed fire may also meet the
condition of ‘‘not reasonably
controllable or preventable’’ by
examining whether there are 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
significant build-up of forest fuels in a
particular area that if left unaddressed
would pose an unacceptable risk of
catastrophic wildfire, which could
result in adverse impacts of much
greater magnitude, duration, and
severity than would result from careful
use of prescribed fire. A particular
ecosystem may also be highly
dependent on a natural fire return
interval 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 prescribed
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 prescribed
fire qualifies as being ‘‘not reasonably
controllable or preventable.’’ Thus, we
believe that a prescribed fire, conducted
by Federal, State, Tribal or private
wildland managers or owners, under the
conditions described above may qualify
as an exceptional event.
In addition, one of the principles
contained in SAFE–TEA–LU, section
6013(b)(3)(A), includes the principle
that States must take necessary
measures to safeguard public health
regardless of the source of air pollution.
We believe it reasonable to tie the
qualifying criteria for an
anthropogenically generated prescribed
fire to State accountability for public
health protection. Consistent with
historical practice governed by the
guidance contained in the ‘‘Interim Air
Quality Policy on Wildland and
Prescribed Fires,’’ issued on May 15,
1998, EPA approval of exceedances
linked to a prescribed fire used for
resource management purposes is
contingent on the State certifying that it
has adopted and is implementing a
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Smoke Management Program (SMP) as
described in that policy. A State SMP
establishes a basic framework of
procedures and requirements for
managing smoke from a prescribed fire
managed for resource benefits. A SMP is
typically developed by a State or Tribe
with cooperation and participation by
wildland managers, both public and
private, and the general public. As
reflected in the Interim Air Quality
Policy on Wildland and Prescribed
Fires, States are provided flexibility on
the structure of a SMP. Thus, a SMP can
be extensive and detailed, or simply
identify the basic smoke management
practices for minimizing emissions, and
controlling impacts from a prescribed
fire.12 In the proposal to this rule, EPA
proposed to continue the use of that
approach. We also proposed to expand
the criteria for contingent approval to a
prescribed fire where, in lieu of a SMP,
basic smoke management practices, that
minimize emissions and control
impacts, are being employed by burners.
In order to protect public health in areas
where a SMP has not been adopted, in
the final rule, the Agency has elected to
expand, on a case-by-case basis, the
qualifying criteria by which a prescribed
fire may qualify as an exceptional event.
In those cases, the Agency will judge on
a case-by-case basis whether the State
has ensured that appropriate basic
smoke management practices have been
employed in determining whether the
prescribed fire qualifies as an
exceptional event. If an exceptional
event occurs using the basic smoke
management practices approach, the
State must undertake a review of their
approach to ensure public health is
being protected and must include
consideration of development of a SMP.
Comments and Responses
Comment: Several commenters
supported classifying prescribed fire as
qualifying as an exceptional event.
However, some commenters indicated
that there should be limitations placed
on when this type of fire should be
considered as an exceptional event. A
number of commenters also
disapproved of allowing prescribed fire
to be considered as an exceptional event
because they believe that this type of
12 Basic smoke management practices could
include, among other practices, steps that will
minimize air pollutant emissions during and after
the burn, evaluate dispersion conditions to
minimize exposure of sensitive populations, actions
to notify populations and authorities at sensitive
receptors and contingency actions during the fire to
reduce exposure of people at such receptors,
identify steps taken to monitor the effects of the fire
on air quality, and identify procedures to ensure
that burners are using basic smoke management
practices.
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fire is anthropogenic and does not meet
the statutory definition of exceptional
event. Some commenters also favored
expanding the criteria for contingent
approval to include instances where
basic smoke management practices are
used in lieu of a SMP, while other
commenters did not favor this
expansion.
Response: The EPA believes that a
prescribed fire may be excluded as an
exceptional event under this rule only
in cases where the event meets the
criteria for an exceptional event as
defined in this rule, if documentation is
submitted to show that the fire meets
the requirement, as described above, of
‘‘affect[ing] air quality,’’ being ‘‘not
reasonably controllable or preventable’’
and ‘‘unlikely to recur at location’’ and
provided the other requirements of the
rule including, among others, the
schedules and procedures for flagging
and demonstration are met. In those
instances where a prescribed fire meets
the criteria for an exceptional event, the
State must also provide appropriate
documentation to show that a certified
SMP was in place or that the burner
employed basic smoke management
practices and that the appropriate
practices were being followed at the
time that the event occurred. Because a
prescribed fire is an anthropogenic
source of emissions for purposes of
section 319, even though it may qualify
as an exceptional event, a State can
attempt to limit the health impact of a
prescribed fire through the thoughtful
development and implementation of a
SMP or ensuring that basic smoke
management practices were employed
that minimize emissions and control
impacts from prescribed fires.
V. The Management of Air Quality Data
Affected by Exceptional Events
The EPA proposed that, in order to
exclude air quality data from
consideration for regulatory purposes,
States must follow the procedures,
timelines, and other requirements
described in the proposed rule. Under
the Final Rule, if an event is determined
to be a qualifying exceptional event
according to section IV.D, a State, Tribe,
or designated local agency may petition
EPA to classify the event as exceptional
and submit a demonstration to justify
data exclusion.13 For data exclusion,
States must clearly identify, or ‘‘flag,’’
13 Although a single qualifying exceptional event
may affect air quality for multiple days and at
multiple monitors, the discussions below consider
an individual demonstration as justifying exclusion
of a single AQS data point. The EPA encourages
State submittals to package demonstrations about
single exceptional events to expedite the review
process.
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data they believe to be influenced by
such events. The demonstration to
justify data exclusion shall provide
evidence that: (a) The event qualifies in
accordance with section IV.D and with
EPA policies and guidance for certain
events as described in section IV.E, (b)
there is a clear causal relationship
between the measurement under
consideration and the event that is
claimed to have affected the air quality
in the area, (c) the event is associated
with an unusual measured
concentration beyond typical
fluctuations including background, and
(d) that there would have been no
exceedance or violation but for the
event.
The SAFE–TEA–LU requirements for
exclusion of data from exceptional
events are: (1) The occurrence of the
exceptional event must be demonstrated
by reliable and accurate data; (2) the
State must show that there is a ‘‘clear
causal relationship’’ between the
NAAQS exceedances and the event; (3)
there must be a public review process
related to the exceptional event
determination; and (4) the rule must set
criteria and procedures for States to
petition EPA to exclude data directly
affected by an exceptional event. The
sections below describe how each of
these requirements must be met.
The sections below address the
flagging of data as exceptional events
that are determined to have affected air
quality, submittal of demonstrations to
request data exclusion, public review,
and the schedule and timing for these
processes. After an exceptional event
occurs (judged according to section
IV.D) and an agency determines that the
event affected ambient air quality,
flagging may occur according to section
V.A. Section V.B describes the
evaluation of whether or not the event
affected ambient air quality. Section V.C
describes the necessary ‘‘but-for’’ test
that data would have complied with the
applicable standard but for the
occurrence of the exceptional event.
Section V.D explains the schedules and
procedures for the flagging and
demonstration submittals, section V.E
discusses the applicability to hourly
readings, section V.F states the
requirements for determination
submittals if the agency requests EPA to
exclude the data from consideration for
regulatory purposes, and section V.G
describes the public review
requirements. Some commenters
suggested that all data occurring from
exceptional events should be flagged,
and EPA will allow these flags for
informational purposes, even if the data
do not qualify for exclusion. If EPA
concurs on the exclusion of data from
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qualifying exceptional events, the data
will be excluded from regulatory
consideration but will still count toward
data capture requirements.
A. Flagging of Data in the AQS Database
1. Background
Air quality data are required,
pursuant to 40 CFR 58.16, 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 database is to
identify those air quality measurements
for which special attention or treatment
is warranted. These include, but are not
limited to, those measurements that are
influenced by exceptional events.
The preamble to the proposed rule
stated: ‘‘In the case of exceptional
events, States place the initial flag on
the data in the AQS database. 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
database 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 stated
previously, 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.’’
2. Final Rule
In the case of exceptional events,
States and Tribes place the initial flag
on the data in the AQS database, but
EPA determines the available flags.14
States may also delegate authority to
14 It is EPA’s intention, for purposes of
consistency with this rule, to review the list of
exceptional events that are currently in the AQS
database following the promulgation of the rule.
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local agencies to submit flags and
documentation. In any event, States
should work with their local agencies
for the identification and review of
exceptional events and consider
requests to flag data from those
agencies. At the time the flag is inserted
into the AQS database, the State must
also provide an initial description of the
event in the AQS comment field. This
initial description should include such
information as the direction and
distance from the event to the air quality
monitor in question, as well as the
direction of the wind on the day in
question. The flags, and the initial event
description, must be inserted into the
AQS database prior to July 1st following
the year in which the event occurred.
Schedules for demonstrations are
discussed in section V.D.
Following an evaluation of the
supporting documentation, EPA will
make a decision concerning whether to
concur with the flag; concurrence will
be marked by the placement of a second
flag in the AQS database by EPA. If EPA
has concurred on the flag, the data will
be excluded from regulatory
determinations such as determinations
related to attainment or nonattainment,
or determinations concerning SIP
development. The EPA will use the
second flag to indicate the following
conditions: EPA concurrence, EPA nonconcurrence, and documentation
submitted with EPA decision pending.
While flagging of the data in the AQS
database by the affected State, local, or
Tribe authority is the first step in an
exceptional events demonstration, it is
insufficient in and of itself to allow for
the exclusion of data. In order for EPA
to concur on an exceptional events flag,
States, Tribes, and local agencies must
meet the additional requirements
described below. As explained, the
State, Tribe, or local agency has the
responsibility to document the
occurrence of the event in question, to
demonstrate that the event qualifies as
an exceptional event in accordance with
section IV.D, is consistent with EPA
policies and guidance for certain events
as described in section IV.E, has
provided for public review in
accordance with section V.G, and to
document the causal connection
between the measurement under
consideration and the event that is
claimed to have affected the air quality
in the area. The State, Tribe, or local
agency must also demonstrate that the
event is associated with an unusual
measured concentration beyond typical
fluctuations including background, and
that there would have been no
exceedance or violation ‘‘but for’’ the
event. Because the initial step of
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flagging the data is a relatively simple
one, States, Tribes, and local agencies
may flag more days than the number of
days for which they ultimately intend to
submit demonstrations to justify data
exclusion.
3. Comments and Responses
Comment: One commenter supported
flagging data related to any fire that
caused an exceedance.
Response: This Rule does not
preclude a State, Tribe, or Local agency
from flagging any data allegedly
influenced by exceptional events.
However, for the data to qualify as an
exceptional event and to exclude it from
regulatory decisions, the data must meet
all of the criteria described in this Rule
and all the procedures delineated must
be followed.
B. What Does It Mean for an Event To
‘‘Affect Air Quality’’?
rmajette on PROD1PC67 with RULES2
1. Background
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 as well as remote
upwind sources. Given the directive in
section 319(b)(3)(B)(ii), that a clear
causal connection must exist between
the ‘‘measured exceedances’’ and the
exceptional event, EPA believes that it
would be unreasonable to exclude data
affected by an exceptional event simply
because of a trivial contribution of an
event to air quality. Furthermore, we
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 costly SIP 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) provides that
there must be a ‘‘clear causal
relationship’’ between a measured
exceedance of a standard and the event
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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) indicates that the
protection of public health is the highest
priority. For these reasons, we proposed
three conditions under which an event
may qualify as ‘‘exceptional’’ for
purposes of special regulatory
consideration: Its air quality impact
must (1) fall both above the level of the
applicable standard (i.e., must be an
‘‘exceedance’’ as required by section
319), (2) be significantly beyond the
normal fluctuating range of air quality,
including background air quality
concentrations, and (3) should be large
enough such that without it there would
have been no exceedance.
We next provided several alternative
approaches to determining whether and
when air quality is ‘‘affected by’’
exceptional events and requested
comment on which of these approaches
was most suitable for demonstrating
such impacts. These approaches
primarily applied to condition (2)
above. Two of the approaches involved
statistical comparisons of existing
flagged data. The final rule most closely
reflects the third proposed option with
some modifications. This option
considered a case-by-case evaluation of
the data against historical, seasonally
adjusted air quality levels. Finally, the
proposed rule provided details
regarding what is meant by an
exceedance (1) and the ‘‘but-for’’
condition (3). These are discussed in
detail in section V.C.
2. Final Rule
Under the Final Rule, the
demonstration to justify data exclusion
must provide a justification that: (a) The
event qualifies in accordance with
section IV.D. and if applicable, with
EPA policies and guidance for certain
events as described in section IV.E, (b)
there is a clear causal relationship
between the measurement under
consideration and the event that is
claimed to have affected the air quality
in the area, (c) the event is associated
with an unusual measured
concentration beyond typical
fluctuations including background, and
(d) there would have been no
exceedance or violation but for the
event (discussed in section V.C). The
second and third criteria establish that
the event affected air quality.
The second criterion that the event
caused an air quality impact may be
shown through a number of methods
including, but not limited to, modeling
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13569
and speciation analysis. The third
criterion distinguishes common events
from those that are exceptional and may
be accomplished through the
presentation of historical evidence.
The final rule permits a case-by-case
evaluation, without prescribed
threshold criteria, to demonstrate that
an event affected air quality. This
demonstration would be based on the
weight of available evidence, but must
consider the historical frequency of
such measured concentrations. While a
State may determine the specific
approach to use for such analysis, it
must compare contemporary
concentrations with the distribution of
all measured data during the past
several years. The evidence that an
event affected air quality may be
presented on a seasonal or other
temporal basis to best compare
contemporary concentrations with the
distribution of historical values. For
consistency with data reporting and
computation of NAAQS statistics, a
calendar quarter basis is suggested.
Baseline data may also be defined
differently for each event type (e.g.,
April and May data may be the most
relevant information for statistical
comparison with certain dust events).
The general statistical approach of
using all measured data during the past
several years is independent of
historical flagging practices and allows
States to accurately represent events not
likely to recur by including all
monitoring data in analyses.
In addition, the magnitude of the
measured concentration on days
affected by exceptional events relative
to historical, temporally adjusted air
quality levels can guide the level of
necessary analysis and documentation
to demonstrate that the event affected
air quality. For extremely high
concentrations relative to historical
values (e.g., concentrations greater than
the 95th percentile), a lesser amount of
documentation or evidence may be
required to demonstrate that the event
affected air quality. The closer the event
concentration is to typical levels (e.g.,
values less than the historical 75th
percentile), the stronger the necessary
evidence would have to be to justify
exclusion of data for regulatory
purposes. This weight of evidence
approach is most nearly analogous to
our historical treatment of exceptional
events.
3. Comments and Responses
Comment: One commenter noted that
EPA’s proposed rule concedes that the
third option would ‘‘provide the least
definitive guidance to assist States in
their evaluations,’’ and ‘‘may make it
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difficult for EPA regions to be consistent
when determining whether to concur on
a flag.’’ Moreover, ‘‘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. While such days
are unlikely to impact short-term
standards, discounting such days can
certainly have an impact on an annual
average concentration.’’ The commenter
asserted that EPA’s description of the
proposed case-by-case evaluation makes
the case for rejecting that option because
it fails to provide the guidance
mandated by section 319, and is so
vague as to be arbitrary.
Response: The EPA disagrees with the
commenter that this option fails to
provide guidance and is so vague as to
be arbitrary. The EPA has explained
above the criteria that it will use in
making its case-by-case evaluations. The
commenter’s concern that the event
must represent concentrations that are
not typically observed is addressed by
the third criterion that the event must be
associated with an unusual measured
concentration beyond typical
fluctuations including background.
Demonstration of the magnitude of the
measured concentrations with respect to
historical frequency under similar
conditions will provide a new level of
consistency across monitoring locations.
Comment: If an area exceeds the
NAAQS, one commenter stated that use
of a 95th percentile criterion better
ensures that the definition of an
exceptional event is met (i.e., unlikely
to recur at a particular location).
Response: The EPA recognizes that
extreme concentrations (e.g.,
corresponding to values greater than the
95th percentile of historical values) are
more likely associated with exceptional
events. With the final rule, we are not
assuming that such values are definitely
exceptional. In fact, some extreme
concentrations may be associated with
various emission sources and
atmospheric conditions which are
unrelated to a causal connection to the
claimed exceptional event. Instead, the
frequency of occurrence relative to
historical concentrations would be used
as an important part of the overall
weight of evidence to demonstrate the
exceptional nature of the claimed air
quality impact.
rmajette on PROD1PC67 with RULES2
C. Use of a ‘‘But For’’ Test
1. Background
There may be instances in which
exceptional events may have a
significant impact on air quality on days
when concentrations are already above
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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 such activities, which
properly fall within the responsibilities
of States to manage for purposes of air
quality attainment and maintenance.
For this reason, we proposed 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 that 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 office to
further discuss this issue.
2. Final Rule
The EPA will maintain the proposed
‘‘but-for’’ requirement that air quality
data may not be excluded except where
States, Tribes, or local agencies show
that exceedances or violations of
applicable standards would not have
occurred ‘‘but for’’ the influence of
exceptional events. Through analyses, it
is possible to demonstrate that an
exceedance or violation would not have
occurred but for the event [See sample
‘‘but-for’’ analysis in memo to docket,
Husar et al. 2006 (https://
www.regulations.gov, EPA–HQ–OAR–
2003–0061–0733 thru 0733.5)]. This
analysis does not require a precise
estimate of the estimated air quality
impact from the event. The weight of
evidence demonstration can present a
range of possible concentrations which
is not as technically demanding as
justifying a specific adjustment to a
measured value.
Because there are two standards for
PM2.5, clarification is needed regarding
the measurements that contributed to an
exceedance or a violation that are
eligible to be excluded. This rule is
limited to values above the annual
standard for PM2.5 because this
simplifies the process for determining
which values are eligible for flagging
according to the intent of section 319.
The short-term PM2.5 NAAQS is based
on a 3-year average of the annual 98th
percentile of 24-hour values. Therefore,
it is possible that one or two of these
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annual concentration values may be
below the level of the NAAQS while the
3-year average is above the level of the
NAAQS. Because three annual 98th
percentile concentration values are
included in the determination of a
short-term PM2.5 NAAQS violation,
individual measurements below the
NAAQS may contribute to a violation.
On the other hand, the annual PM2.5
NAAQS is also a standard based on a 3year average. However, violations of the
annual standard that are caused by
measurements which are not
exceedances of that standard will be
difficult to distinguish from typical air
quality concentrations including
background. To accommodate the 3-year
form of the PM2.5 NAAQS, this rule will
allow measurements whose
concentrations are greater than the level
of the annual NAAQS to be flagged as
being affected by exceptional events for
the purposes of contributing to an
exceedance or violation of the PM2.5
NAAQS. Thus, we provide the
following clarification that individual
measured values greater than the annual
PM2.5 NAAQS will be considered
‘‘exceedances’’ under this rule and
therefore eligible to be considered for
exclusion for comparisons to either the
annual or 24-hour NAAQS.
3. Comments and Responses
Comment: One commenter stated that,
while some of those measurements may
not individually be above the NAAQS,
taken together they might be sufficient
to put an area in violation of an annual
standard. Any ‘‘but for’’ determination
must take into account the aggregate of
exceptional events that occurred within
the applicable NAAQS period.
Response: The rule acknowledges that
it is possible that an event can affect
multiple days. The ‘‘but for’’ provision
allows for data exclusion if but for the
entire event there would have been no
exceedance or violation. Therefore, for
those events that can be shown to affect
air quality on multiple consecutive
days, measurements for the entire
period are eligible for data exclusion,
provided that at least one measurement
day during the episode is an exceedance
as defined by this rule and the air
quality impact on each day are
considered exceptional.
Comment: One commenter cautioned
EPA about using the phrase ‘‘to the
extent it is possible to determine’’
because a ‘‘bright line’’ distinction
between the contribution from natural
and anthropogenic sources often does
not exist.
Response: We agree with this
comment and for this reason we will
permit a weight of evidence-based
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approach to demonstrate that there
would not have been an exceedance or
violation but for the event.
D. Schedules and Procedures for
Flagging and Requesting Exclusion of
Data
1. Background
In establishing procedures and time
tables 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 proposed three
alternatives for public review and
comment. Public comments showed that
each option had desirable aspects, and
these are incorporated into the final
rule.
rmajette on PROD1PC67 with RULES2
2. Final Rule
A multi-step process will be
established for identification of data and
submission of demonstrations. The
process is designed to ensure that
States, Tribes, and local agencies have
adequate opportunity to compile and
present evidence of exceptional and
natural events but also ensures timely
submittals in order to make regulatory
decisions and ensure the protection of
human health through NAAQS
determinations. The steps include State
flagging, annual State submission of an
initial event description, State
submission of a demonstration to justify
data exclusion and EPA review followed
by approval or disapproval. 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 unusual ones,
more time and effort will be needed for
a State, Tribe, or local agency to provide
an adequate demonstration in support of
its request.
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States, Tribes, and local agencies are
encouraged 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 database,
in accordance with the schedule
described in 40 CFR 58.16, which is
generally no later than 90 days after the
end of the calendar quarter. This
includes both flagging of data and
insertion of the initial event description
into the AQS comment field. This
constitutes notification of the
appropriate EPA Regional Office
concerning the State’s intention to seek
exclusion of data. This approach would
ensure that the flagging process remains
consistent with the timeline set forth in
rules governing data submission
requirements. The EPA recognizes that
laboratory analyses may delay these
submissions and therefore is extending
the required time period for submission
to 180 days after the end of the calendar
year (i.e., all flags, along with initial
event descriptions, for a calendar year
must be reported by July 1 of the
following year).
We encourage States, Tribes, and local
agencies to submit the demonstration to
justify data exclusion annually for
exceedances of short-term NAAQS by
July 1. However, the demonstration to
justify data exclusion must also be
submitted no later than 12 months prior
to a regulatory decision. For all flagged
events, the demonstration to justify data
exclusion must be submitted within 3
years of the calendar quarter following
an event, but no later than 12 months
prior to a regulatory decision. This
period should be used primarily to
support NAAQS compliance with
annual averages and violations of the
short-term standard that were not
anticipated. For nonattainment
designations, this would occur with the
Governor’s letter recommending the list
of nonattainment areas. We also
recognize that special circumstances
could dictate more expedited data
delivery, flagging, and minimal
demonstrations (e.g., PM2.5 designations
using 2002–2004 data). The submitted
demonstration to justify data exclusion
as well as the EPA responses and the
rationale for the EPA decision will be
made publicly available through EPA.
The reason for providing the 3-year
timeframe is that for ozone and PM,
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, Tribes, and local
agencies with an opportunity to
evaluate whether the influence of one or
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13571
more exceptional events will be relevant
to determinations of attainment or
nonattainment before undertaking the
effort of preparing and submitting
demonstrations.
Once EPA receives a State’s
demonstration, EPA generally will
undertake to review the demonstration
and provide a concurrence or
nonconcurrence on the flag in the AQS
database within 60 days. The EPA
expects that, in most cases, this time
period should be enough time to review
and provide a concurrence or nonconcurrence related to a State’s request
to exclude data affected by an
exceptional event. However, for more
complex demonstrations, EPA may
require additional time to make its
decision and will notify the State of the
additional time required.
3. Comments and Responses
Comment: One commenter supported
arguments on why the proposed rule
must include a procedure for
retrospective flagging that addresses the
full set of the State’s needs so that the
end result is that the State can flag any
and all events impacted by natural
events.
Response: With the Final Rule, EPA
requires annual submittal of flags. States
may, if they so choose, submit them
sooner. This schedule ensures that data
are collected and retained shortly after
the event and identification of potential
(non-routine) events is done in a timely
fashion to ensure that appropriate
corrective actions can be taken. States
would only maintain minimal
documentation supporting the decision
to flag the data. The full demonstrations,
however, can come later, in order to
allow States time to focus efforts on
those events that are determined to have
an impact on attainment. The Agency
notes that the Exceptional Events Rule
does not apply to routine natural events
that are part of background air quality.
Comment: One commenter was
concerned that a State may have failed
to flag data impacted by a natural event
because the data values were below the
current NAAQS, only to find the State
threatened with nonattainment after
NAAQS revisions.
Response: For data collected before
the effective date of this rule, States may
include a demonstration to justify data
exclusion with the Governor’s
recommendation letter on
nonattainment areas, provided that
there was notice and opportunity for
public comment. After considering this
and other comments, for PM2.5 data
collected during calendar years 2004–
2006, that the State identifies as
resulting from an exceptional event,
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EPA is permitting the State to flag and
submit an initial description of the
event provided that these are submitted
no later than October 1, 2007. In cases
where the State is able to show that this
time period is inadequate, a State may
submit a request for an extension and
EPA will grant this request for an
extension up to but no later than
December 1, 2007. This procedure
should accommodate States concerned
about potential PM2.5 nonattainment
areas using the 2004–2006 data sets. The
EPA may consider a similar exemption
of the schedules for submittal of data for
future revision of standards.
Comment: One commenter stated that
EPA should also make allowances for
those situations when a State neglects to
flag a value or submit documentation
within the required timeframes. In these
cases, the commenter asserted that EPA
should provide some type of petitioning
process.
Response: If a State fails to meet the
schedule for flagging or document
submittal, late petitions will not be
considered. Policy decisions, SIP
planning, and dissemination of data
should not be delayed or altered based
on a State’s failure to submit
documentation or follow the regulatory
procedures in a timely manner.
rmajette on PROD1PC67 with RULES2
E. Exclusion of Entire 24-Hour Value as
Opposed to a Partial Adjustment of the
24-Hour Value
1. Background
In general, EPA’s historical practice
has been to exclude a daily measured
value in its entirety when an
exceptional event causes that value, and
we retained this approach in the
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 for
PM2.5 and is associated with a nearby
forest fire, then EPA is likely to 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 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
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an area affected by a wildfire 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 that 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 precise and universally
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 and its impact on the
requirements set forth in this rule for
determining an exceptional event.
2. Final Rule
We are retaining in this rule EPA’s
historical practice to exclude a daily
measured value in its entirety when that
value is found to be caused by a
qualifying exceptional event that
affected air quality in accordance with
the conditions described in sections V.B
and V.D. If precise and universally
applicable techniques that are
administratively and technically
feasible and that could support partial
adjustment of air quality data become
available in the future, EPA will,
through a rulemaking, propose, and as
appropriate, finalize a technique for
partial adjustment of data as well as any
other matters in this rule which may be
affected by the availability of this
technology.
One exception may be made to this
exclusion of the entire daily value for
monitoring locations with hourly
measurements by Federal Reference
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Methods (FRM), Federal Equivalent
Methods (FEM), and/or Approved
Regional Methods (ARM) where such
data are submitted routinely to AQS.
For example, in cases where
stratospheric ozone intrusion occurs,
those hourly (but not sub-hourly)
measurements affected by the intrusion
may be excluded in order to calculate
the ozone measurements for the day.
The individual hours are to be excluded
however, if the resulting calculated
NAAQS averaging time value exceeds
the level of the standard, not just if the
individual hourly values exceed that
level. Thus, in the case of ozone, the
resulting 8-hour average must exceed
0.08 ppm, and the resulting 24-hour
average must exceed 15.0 µg/m3 for
PM2.5. Incomplete data substitution
protocols shall also be considered when
evaluating the original and revised
NAAQS averaging time value. In other
words, an 8-hour ozone period is
considered valid when fewer than six
valid hours are present if one half the
minimum detection limit can be
substituted for the missing hours and
the resultant 8-hour value still exceeds
0.08 ppm; a daily (24-hour) PM2.5 value
is considered valid when fewer than
eighteen valid hours are present if
zeroes can be substituted for the missing
hours and the resultant 24-hour value
still exceeds 15.0 µg/m3.
3. Comments and Responses
Comment: One commenter supported
value adjustment rather than exclusion
when, and only when, such adjustment
can be accomplished by the application
of various quantitative or semiquantitative approaches. When this is
not possible, the value in question
should be replaced with a long-term
seasonal mean value.
Response: The EPA will consider
such analyses as part of the weight of
evidence to judge ‘‘but-for,’’ but will not
make quantitative adjustments to
reported measured values because EPA
does not believe sufficient quantitative
methods are available at this time.
F. What Should States Be Required To
Submit in Their Exceptional Events
Demonstrations?
1. Background
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
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‘‘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 database, 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,
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. States 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:
• 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.
• Identification of the spatial pattern
of the affected area (the size, shape, and
area of geographic coverage). This could
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include, for instance, the use of satellite
or surface measurement data.
• 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.
• 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.
• High wind speeds 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
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 very likely 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,
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13573
and where emissions associated with
the event are both substantially greater
than and different in composition from
those of other nearby sources.
2. Final Rule
The demonstration to justify data
exclusion will address specific monitor
readings reported to the AQS database.
As stated in the previous sections, a
complete demonstration shall justify
that: (a) The event qualifies in
accordance with section IV.D. and with
EPA policies and guidance for certain
events as described in section IV.E, (b)
there is a clear causal relationship
between the measurement under
consideration and the event that is
claimed to have affected the air quality
in the area, (c) the event is associated
with an unusual measured
concentration beyond typical
fluctuations including background, (d)
there would have been no exceedance or
violation but for the event, and (e) the
State has provided an opportunity for
the public to comment as required
under section V.G. The level of
documentation may vary by the type of
event and can be guided in part by the
relative magnitude of the observed
concentrations. To obtain concurrence,
EPA must determine that the
demonstration is complete and provides
a reasonable technical demonstration.
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 specifying
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. We believe, however, that at a
minimum, the elements of such a
demonstration 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.
Acceptable documentation will be
determined through consultation with
the EPA regional offices. However,
certain minimum requirements (e.g.,
‘‘but for’’ test) will be necessary as
discussed in the earlier sections of this
rule.
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3. Comments and Responses
2. Final Rule
Comment: In cases where high wind
data cannot be found, one commenter
stated that EPA should use a ‘‘weight of
evidence’’ approach, and should
recognize that not accepting a
demonstration that such exceedances
are exceptional events is equivalent to a
determination that the exceedances
were caused by recurring anthropogenic
sources.
Response: The EPA agrees that a
weight of evidence approach is the most
appropriate for demonstrations of
exceptional impact.
Comment: One commenter asserted
that States should be allowed to choose
not to submit any demonstration, if the
flagged value does not impact a
regulatory determination or if more
detailed investigation indicates that the
value may not have been caused by an
exceptional event after all. In these
cases, the agency should have the
option to remove the flag.
Response: We agree that the flag can
be removed in these circumstances or
left for informational purposes only.
Comment: One commenter stated that
EPA must provide a reasonable
explanation and documentation for their
decision to deny any request for the
flagging of data.
Response: The EPA regional offices
will work with the States, Tribes, and
local agencies to ensure that proper
documentation is submitted to justify
data exclusion. The EPA will make the
response and associated explanation
publicly available.
Comment: One commenter stated that
EPA must establish a technically-based
appellate process for States to follow
when Regional Offices do not concur
with a data flag.
Response: The EPA does not believe
that an appellate process is necessary
because we anticipate that the States
and Regional Offices will be working
closely through the data and
documentation submission process.
We are requiring 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 30 days of
public review and comment. The State
or designated local agency should
consider the public comments prior to
the final 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. The EPA does not require
that public hearings be held on
exceptional events demonstrations but
leaves this matter to the States’
discretion consistent with their
administrative procedures. With the
submission of the demonstration, the
State should document that the public
comment process was followed.
G. Public Availability of Air Quality
Data and Demonstrations Related to
Exceptional Events
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1. Background
Section 40 CFR part 58.16 of EPA’s air
quality monitoring rules state that all
ambient air quality data and associated
quality assurance data, including
metadata records and information
specified by the AQS Data Coding
Manual epa.gov/ttn/airs/airsaqs/
manuals/manuals.htm must be reported
to EPA via AQS. This information
includes exceptional event flags.
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3. Comments and Responses
Comment: One commenter stated that
any new rules related to the flagging of
exceptional events should be consistent
with prior EPA policies and provide
sufficient time for States to engage the
public in the process prior to data being
flagged in the AQS.
Response: The EPA believes that the
data demonstration requirements of the
final rule provide sufficient time to
engage the public. Not only does the
final rule require that the public be
accorded an opportunity to comment on
the State’s findings, but in some
instances there will be further
opportunities for public review and
comment at the time that EPA proposes
to base specific actions, e.g., approval or
disapproval of SIP revisions. Thus, we
do not believe that additional public
review and comment provisions are
necessary or appropriate.
VI. Additional Requirements
Pursuant to section 319, EPA is
finalizing this rule to address data that
has been influenced by exceptional
events. Also, EPA is finalizing one of
four options put forth in the proposed
rule to address the issue of whether, and
to what extent, States are required to
adopt specific mitigation plans or
measures to protect the public from
emissions due to exceptional events.
Section 319 states that in promulgating
regulations under the section, EPA shall
follow certain, enumerated principles
and that regulations must contain
certain requirements. Section
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319(b)(3)(A) contains five principles,
including the principle that each State
‘‘must take necessary measures to
safeguard public health regardless of the
source of air pollution.’’ In order to
address this principle, EPA is finalizing
its proposal to exclude trivial and more
routine air quality impacts from
qualifying as an exceptional event and
is also finalizing a ‘‘but for’’ test as a
precondition to qualification as an
exceptional event (See: section V.C
above).
A. Requirements for States To Provide
Public Notification, Public Education,
and Appropriate and Reasonable
Measures To Protect Public Health
1. Background
The EPA proposed one approach and
took comments on three alternative
options concerning what actions a State
should take in anticipation of, or in
response to, the occurrence of an
exceptional event. The options that
were proposed ranged from being very
detailed and prescriptive to being very
flexible and less prescriptive in terms of
the actions that States should take to
mitigate the impact of an exceptional
event on the public. While EPA does not
believe that section 319(b)(3)(A)
explicitly requires, in and of itself, that
States must develop mitigating
measures or plans, EPA solicited
comment in the proposed rule on
whether this subparagraph supports the
use of other legal authority to require
mitigating actions or plans when an
exceptional event occurs, and solicited
comment on issues regarding its legal
authority to require mitigation measures
and plans, and the legal basis for not
requiring mitigation measures or plans.
Option 1 in the proposed rule
provided that in cases where
exceedances of a NAAQS are caused by
an exceptional event, once a State
becomes aware that an exceptional
event is occurring, is predicted to occur,
or has occurred, the State must take
reasonable and appropriate actions to:
• 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.
• 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.
• Take appropriate and reasonable
measures to abate or minimize the
exposure of the public to high
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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. States must review the need to
implement controls on contributing
anthropogenic sources on a case-by-case
basis. 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 option 1, EPA also proposed
that, where a State is requesting that air
quality data be excluded as an
exceptional event, the State must
submit, as a part of its demonstration,
appropriate documentation to show that
the State provided public notice and
public education concerning the event
in question, and that the State took
reasonable and appropriate measures to
abate or minimize the exposure of the
public to the emissions from the event,
where appropriate.
Option 2 in the proposed rule
provided that, States are 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. Under
this option, States would be required to
develop and adopt the general
requirements and procedures necessary
for the implementation of a mitigation
plan to address exceptional events as a
part of its section 110(a)(1) SIP to
address a new or revised NAAQS. The
general plan related to exceptional
events would include provisions
providing for public notice, public
education related to an event, and
provide a requirement for a State to take
reasonable and appropriate measures to
mitigate the public health impacts of an
exceptional event. Under this option, in
cases where control measures are
required to address the impacts
associated with an exceptional event,
the State would be required to
implement appropriate measures on an
episodic basis, meaning in response to
a specific event that affects the air
quality of a particular area.
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Option 3 in the proposed rule
required that, 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
option 2 above, which would require
each State to adopt a plan under section
110(a)(1) of the CAA which would
contain the general provisions of a
mitigation plan in advance of the
occurrence of any exceptional event.
Under option 3, the mitigation plan
would only be developed by the State
following the occurrence of an
exceptional event for which the State
requested exclusion of the air quality
data, and would not be submitted as a
part of the SIP. The mitigation plan
would be required to address the actions
that would be taken by the State related
to future similar events. The mitigation
plan under this option would have the
same provisions as required of 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.
Option 4 provided that 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. This
approach proposed to 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, under this proposed option States
would not be obligated to take any
particular actions to mitigate exposures
such as those contained in Option 1, to
develop and implement a formal
mitigation plan as part of the SIP such
as those contained in Option 2, or to
develop a more formal plan with
requirements not a part of the SIP such
as those contained in Option 3.
2. Final Rule
The EPA is adopting a modified
version of Option 1 from the proposed
rule, as described above. This option
does not require States to submit formal
mitigation plans; however, States must
provide public notice, public education,
and must provide for implementation of
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reasonable measures to protect public
health when an event occurs.
3. Comments and Responses
Comment: Several commenters
supported option 1 because they stated
that it provides more flexibility for
States to determine the appropriate
measures to be implemented related to
the occurrence of an exceptional event.
Other commenters supported option 1
for well defined, well understood events
that are non-recurring or unlikely to
recur. The majority of the commenters
who commented on option 2 strongly
opposed that option. The commenters
indicated that option 2 would waste
scarce local resources in developing a
mitigation plan. Other commenters
stated that issues concerning
exceptional events should be dealt with
outside the SIP process and section 110
of the CAA. With regard to Option 3,
one commenter indicated that a
preemptive plan similar to a Natural
Events Action Plan (NEAP) (which
includes Reasonably Available Control
Measures (RACM)/Best Available
Control Measures (BACM) is necessary
to mitigate the poor air quality impacts
associated with exceptional events. The
commenter stated that BACM, not
RACM, must be implemented on all
contributing anthropogenic sources
related to an exceptional event. Several
commenters supported option 3 for
addressing public health impacts related
to recurring natural events. The
commenters stated that mitigation plans
should include BACM for contributing
anthropogenic sources, not RACM. The
majority of commenters who
commented on option 4 stated that they
supported the implementation of option
4 because it allows States the most
flexibility for developing and tailoring
programs for public notification of
exceptional events, the implementation
of education programs on exceptional
events, and implementation of
reasonable measures to protect public
health.
Response: States have an inherent
responsibility to protect its citizens and
as such to provide appropriate and
reasonable actions to mitigate the
impact of exceptional events on the
public health. This includes alerting the
public when such events occur,
providing public education concerning
the health effects of such events, and
implementing reasonable measures to
mitigate the impact of such events on
public health. Consistent with this
inherent responsibility, it is EPA’s belief
that States are in a better position to
make decisions concerning what actions
should be taken to protect the public
when an exceptional event occurs. This
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being the case, States should have the
necessary flexibility to take appropriate
actions when exceptional events occur.
The EPA is adopting a modified version
of its proposed preferred option 1,
which requires States to provide public
notification, public education, and
provides that States should take
‘‘reasonable and appropriate measures’’
to protect public health related to the
occurrence of an event. Because States
are inherently responsible for the public
health of its citizens, and are capable of
making the determinations of what
actions should be taken to mitigate the
impact of such events on the public
when they occur. The EPA has modified
option 1 from the proposed rule and
will not be requiring States to submit
documentation concerning the actions
that it took to mitigate the impact of
exceptional events, in order for EPA to
exclude data from regulatory
consideration. As proposed in option 1,
States may still make determinations
regarding reasonable measures in a
particular instance, which may or may
not include the implementation of
control measures on contributing
anthropogenic sources related to an
event, and are not limited to any
particular measure. Therefore, under
this option the implementation of
RACM or BACM is not required, but a
State has the necessary flexibility to
determine if, and what, controls should
be implemented following an event, as
well as the level of control that is
required. The EPA believes that this
modified option 1 provides suitable
flexibility to allow States to take those
actions that it deems necessary and
appropriate to protect public health.
While section 319, as revised by SAFE–
TEA–LU, does not specifically provide
that States must implement mitigation
plans, in developing the exceptional
events rule, EPA is required to consider
the enumerated principles including the
principle that States must take
necessary measures to protect public
health regardless of the source of air
pollution. Therefore, under the
modified version of option 1 adopted in
this final rule, States must take
reasonable and appropriate actions to
protect public health.
Comment: Several commenters stated
that the exceptional events rule should
be consistent with the current
requirements under existing policies
with respect to the need for a NEAP to
address recurring natural events such as
high wind events.
Response: The EPA believes that it is
advantageous for States to keep NEAPs
in place that are currently being
implemented in order to address the
public health impacts associated with
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recurring natural events such as high
wind events. However, following the
promulgation of this rule, States will no
longer be required to keep NEAPs in
place that were not approved as a part
of a SIP for an area. Where a NEAP, as
well as BACM, has been approved as a
part of a nonattainment SIP for an area,
the NEAP, as well as the associated
BACM, must remain in place. States
may, however, submit a request to EPA
to remove the NEAP and BACM from
the SIP. The request must contain an
approvable demonstration, as required
by section 110(l), which shows that the
removal of the NEAP and BACM will
not interfere with any applicable
requirement concerning attainment or
maintenance of the NAAQS for an area,
reasonable further progress, or any other
applicable requirement for the area.
VII. Special Treatment of Certain
Exceptional Events Under This Final
Rule
As stated in section IV.D above, this
final 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 of the NAAQS in an
affected area. This final rule applies to
several types of natural events,
including, but not limited to, volcanic
and seismic activities, natural disasters,
high wind events, certain fires, and
stratospheric ozone intrusions. It also
applies to transported pollution
originating from national and
international sources that otherwise
meets the criteria and requirements for
exceptional events. Some types of
exceptional events have unusual
characteristics that require special
consideration in the context of this final
rulemaking. We discuss each of these
special issues, and the necessary
accommodations, below.
A. Volcanic and Seismic Activities
1. Background
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 that it is appropriate to
consider an extended timeframe for
flagging and exclusion of data
associated with such events.
Specifically, EPA believes that
emissions attributed to anthropogenic
activities associated with clean-up that
re-entrain volcanic ash and dust from
seismic activity during the first year (12
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months) following an event will be
treated as due to the natural event.
2. Final Rule
The EPA is finalizing its proposal
with regards to volcanic and seismic
activities. The EPA will allow up to 12
months for the clean-up of ash deposits
due to volcanic/seismic events. During
that time period, emissions of reentrained dust due to anthropogenic
activities associated with cleanup may
be treated as exceptional events. In
cases where the damage caused by the
event is so substantial that a 12-month
period is inadequate to address the
clean-up that is necessary, a State may
submit a request for an extension of the
12-month time period to EPA. As stated
elsewhere in this rule, EPA will grant
requests for extensions of the time
period related to such events on a caseby-case basis. States are encouraged to
submit supporting information
concerning the reason for the extension
and the length of time being requested
for the extension.
B. High Wind Events
1. Background
Where high wind events result in
exceedances or violations of the
particulate matter standards, EPA
proposed that they be treated as natural
events if there is a clear causal
relationship demonstrated between the
exceedances measured at the air quality
monitoring site and the high wind event
in question, and if anthropogenic
activities which contribute to
particulate matter emissions in
conjunction with the high wind event
are reasonably well-controlled.
2. Final Rule
The EPA’s final rule concerning high
wind events states that ambient
particulate matter concentrations due to
dust being raised by unusually high
winds will be treated as due to
uncontrollable natural events where (1)
the dust originated from
nonanthropogenic sources, or (2) the
dust originated from anthropogenic
sources within the State, that are
determined to have been reasonably
well-controlled at the time that the
event occurred, or from anthropogenic
sources outside the State. These events
are also discussed in section IV.E.5.c
above. In cases where anthropogenic
sources are determined to have
contributed to exceedances or violations
due to high wind events at air quality
monitoring sites, per our decision in
this rulemaking concerning the action
that States must take to mitigate the
impact of exceptional events on public
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health (See section VI above), States
must take reasonable and appropriate
measures to mitigate the impact
associated with the event on public
health. As stated in section VI of this
rule, States have the flexibility to
implement reasonable measures to
protect public health when an
exceptional event occurs. These actions
may or may not include the
implementation of controls on
contributing anthropogenic sources
related to an event. However, where
anthropogenic sources have contributed
to the exceedances of the PM NAAQS at
an air quality monitoring site due to a
high wind event, a State must take
reasonable and appropriate measures to
protect public health.
Since the conditions that cause or
contribute to high wind events vary
from area to area with soil type,
precipitation, and the speed of wind
gusts, States should provide appropriate
documentation which indicates what
types of circumstances contributed to
the exceedances or violations at the
monitoring site in question.15 In this
rule, EPA is not identifying a specific
wind speed which should be considered
when making a determination
concerning whether an event should
qualify as exceptional. Instead, EPA is
requiring that States submit appropriate
documentation which demonstrates
why a particular event should be
considered exceptional for the affected
area. The EPA will review the
documentation submitted by States
concerning high wind events and will
make decisions concerning whether to
exclude the data as being influenced by
15 Section 319(b)(1)(B) states: ‘‘In this subsection,
the term ‘exceptional event’ does not include (i)
stagnation of air masses or meteorological
inversions; (ii) a meteorological events involving
high temperatures or a lack of precipitation; or (iii)
air pollution relating to source noncompliance.’’ In
terms of the exclusion related to ‘‘a meteorological
event involving high temperatures or a lack of
precipitation’’ EPA believes that this statutory
language prohibits EPA from treating a typical dry
day(s) or a dry season for an area as an exceptional
event. However, EPA believes that Congress did not
intend that the above quoted language to prevent a
State from submitting compelling documentation
which shows that severe drought conditions may
have contributed to an exceptional event, but
instead was designed to prevent the indiscriminate
exclusion of data on days characterized by ‘‘high
temperature and a lack of precipitation.’’ Therefore,
EPA is permitting States to submit documentation
which shows that ‘‘severe drought’’ conditions may
have contributed to the occurrence of a high wind
event. The documentation must, however, be
compelling enough to show that the conditions
present at the time of the event were more
substantial than a typical dry day(s) or dry season
for the area in question, but were related to severe
drought conditions. The EPA will review this
information and make decisions concerning the
exclusion of the data related to the event on a caseby-case basis.
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an exceptional event on a case-by-case
basis.
C. Stratospheric Ozone Intrusion
1. Background
Consideration of stratospheric ozone
intrusions applies only to the 8-hour
ozone standard. The occurrence of such
intrusions are extremely difficult to
measure or document given currently
measured meteorological parameters
and the locations of these
measurements. The infrequency, short
durations, and localized nature of such
events makes it difficult to use currently
available, general meteorological data,
which are usually collected at isolated
locations such as airports, to determine
whether a stratospheric ozone intrusion
has occurred. The EPA believes that 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.
2. Final Rule
The EPA is finalizing its rule as
proposed. The EPA’s determination of
whether a stratospheric ozone intrusion
has occurred will be made on a case-bycase basis based on reasonable judgment
considering the criteria as noted above.
It is our intention to review this type of
exceptional event during the next
review of the NAAQS for ozone. A
review of historical data related to the
flagging of stratospheric ozone intrusion
as an exceptional event shows that the
event has only been flagged on a few
isolated occasions.
VIII. Treatment of Fireworks Displays
A. Background
The EPA proposed to treat emissions
due to fireworks displays in a manner
similar to exceptional events. Some
national and/or cultural traditions, such
as July 4th Independence Day and the
Chinese New Year, have long included
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fireworks displays as important
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 determinations.
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, to explore the use of lower
emitting fireworks, as well as to manage
associated activities that may also have
significant air quality impacts in the
areas where these events are held. Such
precautions 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. For these
reasons, where States can show that the
use of fireworks displays was integral to
significant traditional national, ethnic,
or other cultural events, we proposed
that air quality data associated with
such events could be excluded similar
to exceptional events under this rule.
B. Final Rule
The EPA is finalizing the approach as
stated in the proposed rule to treat
emissions from fireworks similar to the
treatment of exceptional events in the
final rule provided that the event meets
the other criteria as stated in this
rulemaking. For example, the event
must be determined to have affected air
quality. Where a State can show that the
use of fireworks is significantly integral
to traditional national, ethnic, or other
cultural events (e.g., July Fourth
celebrations, Chinese New Year
celebrations, Diwali, etc.), EPA will
exclude data from regulatory
determinations for monitoring stations
whose exceedances or violations has
been determined to be caused by
emissions from fireworks displays on a
case-by-case basis. As stated in other
parts of the rule, States must assure that
reasonable measures were taken to
protect the public from the emissions
created by the fireworks display. Under
this rule, States are also strongly
encouraged to institute educational
programs that alert the public to the
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health effects associated with exposure
to emissions from fireworks displays.
C. Comments and Responses
Comment: The majority of
commenters who commented on this
issue agreed that emissions from
fireworks should be treated as an
exceptional event. However, some
commenters disagreed with EPA’s
proposal to treat fireworks as an
exceptional event. Several commenters
believed that fireworks are neither an
exceptional event nor a natural event
and that EPA should not make
provisions for fireworks to be excluded
as an exceptional event.
Response: In considering the intent of
the SAFETEA–LU legislation, it is EPA’s
belief that Congress did not intend to
prohibit the exclusion of data affected
by emissions from fireworks related to
celebrations of national or cultural
traditions. It is EPA’s belief that data
influenced by fireworks displays should
be subject to the same provisions as
other exceptional events identified
under this rule. Therefore, the
mitigation actions described in section
VI.A above would also apply to
emissions related to fireworks displays.
IX. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
significant regulatory action because it
raises novel legal or policy issues
arising out of legal mandates.
Accordingly, EPA submitted this action
to the Office of Management and Budget
(OMB) for review under Executive
Order 12866 and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
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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 database, and to justify data that
has been flagged as being affected by
exceptional or natural events. However,
the OMB has previously approved the
information collection requirements
regulations for ambient air monitoring
contained in 40 CFR part 58, 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
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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.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedures Act 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 this final rule
on small entities, small entity is defined
as: (1) A small business as defined by
the Small Business Administration’s
regulations at 13 CFR 121.201; (2) a
small governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
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
(DC Cir., 2000), cert. den., 532 U.S. 903
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(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 during and following an
exceptional or natural event. Because
affected States would have discretion to
implement controls on sources that may
need to be regulated due to
anthropogenic contribution 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 this final rule on small
entities, I certify that this rule will not
have a significant economic impact on
a substantial number of small entities.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal Agencies to assess the effects of
their regulatory actions on State, local
and Tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State
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
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development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small government on compliance with
regulatory requirements.
We have determined that this rule
does not contain a Federal mandate that
may result in expenditures of $100
million or more for State, local, and
Tribal governments, in the aggregate, or
the private sector in any 1 year. 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. Thus, this rule is not subject to
the requirements of sections 202, 203,
and 205 of the UMRA.
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E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, 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 final rule does not have
federalism implications. It will not have
substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. The CAA
establishes the scheme whereby States
take the lead in developing plans to
meet the NAAQS. Thus, Executive
Order 13132 does not apply to this rule.
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 final 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
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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 through
the Tribal Implementation Plan (TIP).
This rule does not have Tribal
implications as defined by Executive
Order 13175. It does not have a
substantial direct effect on one or more
Indian Tribes, because no Tribe has
implemented a TIP related to the PM or
the 8-hour ozone 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.
However, even though we found that
this rule does not have Tribal
implications, we nevertheless were
aware of Tribes that had an interest in
this rule. Therefore, we conducted
communications and outreach related to
the rule with the Tribes through
discussions via conference calls with
the Tribal Association. We also
provided information to the Tribes on
the rule via the Quarterly Tribal Air
Newsletter.
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
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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.
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.
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.
J. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
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Register. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This action is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2). This rule will be effective May
21, 2007.
K. Petitions for Judicial Review
Under section 307(b)(1) of the CAA,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the District of
Columbia Circuit by May 21, 2007.
Filing a petition for reconsideration by
the Administrator of this final rule does
not affect the finality of this rule for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review must be filed, and
shall not postpone the effectiveness of
such rule or action. This action may not
be challenged later in proceedings to
enforce its requirements. See CAA
Section 307(b)(2).
List of Subjects
40 CFR Part 50
Environmental protection, Air
pollution control, National parks,
Wilderness areas.
40 CFR Part 51
Environmental protection, Air
pollution control, Administrative
practice and procedure, Reporting and
recordkeeping requirements.
Dated: March 14, 2007.
Stephen L. Johnson,
Administrator.
In consideration of the foregoing, the
Environmental Protection Agency
amends 40 CFR parts 50 and 51 as
follows:
I
PART 50—NATIONAL PRIMARY AND
SECONDARY AMBIENT AIR QUALITY
STANDARDS
1. The authority citation for part 50
continues to read as follows:
I
Authority: 42 U.S.C. 7401 et seq.
2. Amend § 50.1 to add paragraphs (j)
and (k) to read as follows:
I
§ 50.1
Definitions.
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*
*
*
*
*
(j) Exceptional event means an event
that affects air quality, is not reasonably
controllable or preventable, is an event
caused by human activity that is
unlikely to recur at a particular location
or a natural event, and is determined by
the Administrator in accordance with 40
CFR 50.14 to be an exceptional event. It
does not include stagnation of air
masses or meteorological inversions, a
meteorological event involving high
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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
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.
I
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 standard
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) Demonstration to justify data
exclusion may include any reliable and
accurate data, but must demonstrate a
clear causal relationship between the
measured exceedance or violation of
such standard and the event in
accordance with paragraph (c)(3)(iii) of
this section.
(b) Determinations by EPA. (1) EPA
shall exclude data from use in
determinations of exceedances and
NAAQS violations where a State
demonstrates to EPA’s satisfaction that
an exceptional event caused a specific
air pollution concentration in excess of
one or more national ambient air quality
standards at a particular air quality
monitoring location and otherwise
satisfies the requirements of this
section.
(2) EPA shall exclude data from use
in determinations of exceedances and
NAAQS violations where a State
demonstrates to EPA’s satisfaction that
emissions from fireworks displays
caused a specific air pollution
concentration in excess of one or more
national ambient air quality standards at
a particular air quality monitoring
location and otherwise satisfies the
requirements of this section. Such data
will be treated in the same manner as
exceptional events under this rule,
provided a State demonstrates that such
use of fireworks is significantly integral
to traditional national, ethnic, or other
cultural events including, but not
limited to July Fourth celebrations
which satisfy the requirements of this
section.
(3) EPA shall exclude data from use
in determinations of exceedances and
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Frm 00022
Fmt 4701
Sfmt 4700
NAAQS violations, where a State
demonstrates to EPA’s satisfaction that
emissions from prescribed fires caused
a specific air pollution concentration in
excess of one or more national ambient
air quality standards at a particular air
quality monitoring location and
otherwise satisfies the requirements of
this section provided that such
emissions are from prescribed fires that
EPA determines meets the definition in
§ 50.1(j), and provided that the State has
certified to EPA that it has adopted and
is implementing a Smoke Management
Program or the State has ensured that
the burner employed basic smoke
management practices. If an exceptional
event occurs using the basic smoke
management practices approach, the
State must undertake a review of its
approach to ensure public health is
being protected and must include
consideration of development of a SMP.
(4) [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.]
(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 database in 40 CFR 58.16.
(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,
following the State’s submittal of its
demonstration pursuant to paragraph
(c)(3) of this section and EPA review,
EPA notifies the State of its concurrence
by placing a concurrence flag in the
appropriate field for the data record in
the AQS database.
(iii) Flags placed on data as being due
to an exceptional event together with an
initial description of the event shall be
submitted to EPA not later than July 1st
of the calendar year following the year
in which the flagged measurement
occurred, except as allowed under
paragraph (c)(2)(iv) of this section.
(iv) For PM2.5 data collected during
calendar years 2004–2006, that the State
identifies as resulting from an
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exceptional event, the State must notify
EPA of the flag and submit an initial
description of the event no later than
October 1, 2007. EPA may grant an
extension, if a State requests an
extension, and permit the State to
submit the notification of the flag and
initial description by no later than
December 1, 2007.
(v) When EPA sets a NAAQS for a
new pollutant, or revises the NAAQS for
an existing pollutant, it may revise or
set a new schedule for flagging data for
the initial designation of areas for those
NAAQS.
(3) Submission of demonstrations.
(i) A State that has flagged data as
being due to an exceptional event and
is requesting exclusion of the affected
measurement data shall, after notice and
opportunity for public comment, submit
a demonstration to justify data
exclusion to EPA not later than the
lesser of, 3 years following the end of
the calendar quarter in which the
flagged concentration was recorded or,
12 months prior to the date that a
regulatory decision must be made by
EPA. A State must submit the public
comments it received along with its
demonstration to EPA.
(ii) A State that flags data collected
during calendar years 2004–2006,
pursuant to paragraph (c)(2)(iv) of this
section, must adopt the procedures and
VerDate Aug<31>2005
14:06 Mar 21, 2007
Jkt 211001
requirements specified in paragraph
(c)(3)(i) of this section and must include
a demonstration to justify the exclusion
of the data not later than the submittal
of the Governor’s recommendation letter
on nonattainment areas.
(iii) The demonstration to justify data
exclusion shall provide evidence that:
(A) The event satisfies the criteria set
forth in 40 CFR 50.1(j);
(B) There is a clear causal relationship
between the measurement under
consideration and the event that is
claimed to have affected the air quality
in the area;
(C) The event is associated with a
measured concentration in excess of
normal historical fluctuations, including
background; and
(D) There would have been no
exceedance or violation but for the
event.
(iv) With the submission of the
demonstration, the State must document
that the public comment process was
followed.
(v) [Reserved.]
(A) [Reserved]
PART 51—NATIONAL PRIMARY AND
SECONDARY NATIONAL AMBIENT AIR
QUALITY STANDARDS
4. The authority citation for part 51
continues to read as follows:
I
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Frm 00023
Fmt 4701
Sfmt 4700
13581
Authority: 23 U.S.C. 101; 42 U.S.C. 7401–
7671q.
5. Adding Subpart Y consisting of
§ 51.930 to read as follows:
I
Subpart Y—Mitigation Requirements
§ 51.930
Mitigation of Exceptional Events.
(a) A State requesting to exclude air
quality data due to exceptional events
must take appropriate and reasonable
actions to protect public health from
exceedances or violations of the
national ambient air quality standards.
At a minimum, 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; and
(3) Provide for the implementation of
appropriate measures to protect public
health from exceedances or violations of
ambient air quality standards caused by
exceptional events.
(b) [Reserved]
[FR Doc. E7–5156 Filed 3–21–07; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 72, Number 55 (Thursday, March 22, 2007)]
[Rules and Regulations]
[Pages 13560-13581]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-5156]
[[Page 13559]]
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Part II
Environmental Protection Agency
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40 CFR Parts 50 and 51
Treatment of Data Influenced by Exceptional Events; Final Rule
Federal Register / Vol. 72, No. 55 / Thursday, March 22, 2007 / Rules
and Regulations
[[Page 13560]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 50 and 51
[EPA-HQ-OAR-2005-0159; FRL-8289-5]
RIN 2060-AN40
Treatment of Data Influenced by Exceptional Events
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: This action finalizes 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 finalizing the proposal
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. The EPA is also requiring States to
take reasonable measures to mitigate the impacts of an exceptional
event.
DATES: This final rule is effective May 21, 2007.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-HQ-OAR-2005-0159. All documents in the docket are
listed on the https://www.regulations.gov Web site. Although listed in
the index, some information is not publicly available, i.e.,
confidential business information (CBI) or other information whose
disclosure is restricted by statute. Certain other material, such as
copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically through https://
www.regulations.gov or in hard copy at the OAR Docket, EPA/DC, EPA
West, Room 3334, 1301 Constitution Ave., NW., Washington, DC. The
Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the Air
and Radiation Docket and Information Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: General questions regarding the final
rule should be addressed to Mr. Larry D. Wallace, PhD, 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 final rule should be addressed to Mr. Neil Frank, Office of Air
Quality Planning and Standards, Air Quality Assessment Division, Mail
Code C304-01, Research Triangle Park, NC 27711; telephone (919) 541-
5560, and e-mail address frank.neil@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
Regulated Entities. This final rule will affect State and local air
quality agencies. This rule may also affect Tribal air quality agencies
that have implemented air quality monitoring networks or have authority
to implement air quality programs.
This list is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
action. This list gives examples of the types of entities EPA is now
aware could potentially be regulated by this action. Other types of
entities not listed could also be affected. To determine whether your
facility, company, business, organization, etc., is regulated by this
action, you should examine the applicability criteria in section IV of
this preamble. If you have any questions regarding the applicability of
this action to a particular entity, consult the people listed in the
preceding section.
B. How Is This Preamble Organized?
Table of Contents
The following is an outline of the preamble.
I. General Information
A. Does This Action Apply to Me?
B. How Is This Preamble Organized?
II. Preamble Glossary of Terms and Acronyms
III. Background and Purpose of This Rulemaking
A. Legislative Requirements
B. Historical Experience Concerning Exceptional and Natural
Events
IV. This Final Action
A. To Whom and to What Pollutants Does This Rule Apply?
B. How Does This Rule Relate to Indian Tribes?
C. Comments Submitted on the Proposed Rule
D. What Is an Exceptional Event?
E. 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. Natural Disasters and Associated Clean-Up Activities
b. Volcanic and Seismic Activities
c. High Wind Events
d. Wildland Fires
e. Stratospheric Ozone Intrusions
6. Prescribed Fire
V. The Management of Air Quality Data Affected by Exceptional Events
A. Flagging of Data in the AQS Database
1. Background
2. Final Rule
3. Comments and Responses
B. What Does It Mean for an Event to ``Affect Air Quality''?
1. Background
2. Final Rule
3. Comments and Responses
C. Use of a ``But For'' Test
1. Background
2. Final Rule
3. Comments and Responses
D. Schedules and Procedures for Flagging and Requesting
Exclusion of Data
1. Background
2. Final Rule
3. Comments and Responses
E. Exclusion of Entire 24-Hour Value as Opposed to a Partial
Adjustment of the 24-Hour Value
1. Background
2. Final Rule
3. Comments and Responses
F. What Should States Be Required To Submit in Their Exceptional
Events Demonstrations?
1. Background
2. Final Rule
3. Comments and Responses
G. Public Availability of Air Quality Data and Demonstrations
Related to Exceptional Events
1. Background
2. Final Rule
3. Comments and Responses
VI. Additional Requirements
A. Requirements for States To Provide Public Notification,
Public Education, and Appropriate and Reasonable Measures To Protect
Public Health
1. Background
2. Final Rule
3. Comments and Responses
VII. Special Treatment of Certain Exceptional Events Under This
Final Rule
A. Volcanic and Seismic Activities
1. Background
2. Final Rule
B. High Wind Events
1. Background
2. Final Rule
C. Stratospheric Ozone Intrusion
1. Background
2. Final Rule
VIII. Treatment of Fireworks Displays
[[Page 13561]]
A. Background
B. Final Rule
C. Comments and Responses
IX. 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
J. Congressional Review Act
K. Petitions for Judicial Review
II. Preamble Glossary of Terms and Acronyms
The following are abbreviations of terms used in the preamble.
ARM Approved Regional Methods.
AQS Air Quality System.
BACM Best Available Control Measures.
CAA Clean Air Act.
CAAA Clean Air Act Amendments.
EPA Environmental Protection Agency.
FEM Federal Equivalent Methods.
FIP Federal Implementation Plan.
FR Federal Register.
FRM Federal Reference Methods.
NAAQS National Ambient Air Quality Standards.
NEAP Natural Events Action Plan.
NEPA National Environmental Policy Act.
NTTA National Technology Transfer Advancement Act of 1995.
OAQPS Office of Air Quality Planning and Standards.
OMB Office of Management and Budget.
PM Particulate matter.
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 Program.
TAR Tribal Authority Rule.
TIP Tribal Implementation Plan.
UMRA Unfunded Mandates Reform Act.
USDA U.S. Department of Agriculture.
VCS Voluntary Consensus Standards.
III. Background and Purpose of This Rulemaking
A. Legislative Requirements
We \1\ are finalizing 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, required EPA to publish the proposed rule in the
Federal Register no later than March 1, 2006.\2\ Further, EPA must
issue this final rule no later than 1 year from the date of proposal.
The EPA published the proposed rule on March 10, 2006 (See 71 FR
12592).
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\1\ The U.S. Environmental Protection Agency.
\2\ 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.
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In this final rule, EPA is establishing 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 an event that is not reasonably controllable or
preventable; is an event caused by human activity that is unlikely to
recur at a particular location or a natural event; and is determined by
EPA 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 temperatures 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.\3\ 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 exceedances or violations of the NAAQS.
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\3\ 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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The term exceedance refers to a measured or modeled concentration
greater than the level of one or more for a pollutant. The NAAQS are
also set with particular averaging periods (e.g., 3 years for ozone and
PM2.5) such that a violation of the NAAQS for ozone and
PM2.5 requires an average annual concentration level
specified by appendix I and N to 40 CFR 50 to be greater than the level
of the NAAQS. Public comments favored the consideration of data
contributing to both exceedances and violations for data exclusion
under this Rule. As discussed in section V.C, exceedances of any NAAQS
will be eligible for consideration for data exclusion and any data
contributing to violations of daily or sub-daily standards will also be
eligible for consideration (e.g. 8-hour or 24-hour standards). Data
contributing to annual violations without being exceedances themselves
are considered too close to background air quality levels for exclusion
under this Rule.
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 database 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, Congress sought to provide
statutory relief to States to allow them to avoid being designated as
nonattainment or to avoid continuing to be designated
[[Page 13562]]
nonattainment as a result of exceptional events in appropriate
circumstances. 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.
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,
``Guideline for the Interpretation of Air Quality Standards,''
Guideline No. 1.2-008 (revised February 1977).\4\
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\4\ ``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.\5\ 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 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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\5\ 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 are 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).\6\
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\6\ Memorandum from Mary D. Nicols, Assistant Administrator for
Air and Radiation, to EPA Regional Offices entitled, ``Areas
Affected by PM10 Natural Events,'' May 30, 1996.
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On July 18, 1997, EPA issued a 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 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, related to the ozone standard, addresses the treatment of data
determined to be influenced natural events, and section 1.0(b) of
appendix N, related to the PM2.5 standard, provides that EPA
may give special consideration to data determined to be affected by an
exceptional or natural event.
Appendices K, I, and N, which are parts 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) database for use in making regulatory decisions, in some cases it
may be appropriate for EPA 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.\7\ 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.\8\
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\7\ ``Guideline on Data Handling Conventions for the PM NAAQS,''
United States Environmental Protection Agency, Office of Air Quality
Planning and Standards, Research Triangle Park, NC 27711, EPA-454/R-
98-017, December 1998.
\8\ Following the promulgation of this rule, it is EPA's
intention to begin the process to revise the ``Interim Air Quality
Policy on Wildland and Prescribed Fires'' in calendar year 2007 to
update the policy and to ensure that the policy is consistent with
this final rulemaking action. In addition, it is EPA's intent that
agricultural prescribed burning will be addressed when this policy
is updated and will also address basic smoke management practices.
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IV. This Final Action
A. To Whom and to What Pollutants Does This 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 database. 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
[[Page 13563]]
responsible for reviewing and approving or disapproving any requests
for such consideration. Therefore, this final rule applies 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 rule governs 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 rule would govern those
actions as well.
At present, only the NAAQS for ozone and particulate matter (PM)
contain provisions which allow for the special handling of air quality
data affected by exceptional and natural 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 only
applying the provisions of this rule initially to ozone and PM.\9\ 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 provisions 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. We
also intend to use our discretion under this rule to address
determinations for the ozone standard related to the treatment of data
influenced by both exceptional and natural events. Currently, appendix
I, only addresses the treatment of data determined to be influenced by
a stratospheric ozone intrusion and other natural events, but does not
address the handling of data influenced by other exceptional events.
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\9\ Section IV.G of the preamble to the Proposed Rule discussed
special considerations relevant to a new NAAQS for
PM10-2.5 proposed by EPA on December 20, 2005. This
proposed standard would have drawn a distinction between coarse
particles of urban versus non-urban origin, which raised new issues
about the handling of exceedances of the coarse particle standard
caused by exceptional events. However, in EPA's final rule on the PM
NAAQS, issued September 21, 2006, EPA retained the existing 24-hour
PM10 standard instead of promulgating the proposed
PM10-2.5 standard. Thus, section IV.G of the preamble to
the Proposed Rule is no longer relevant and has been removed from
this Preamble.
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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).
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
final 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 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 rule). The EPA intends to work with Tribes on the implementation
of this 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 rule.
C. Comments Submitted on the Proposed Rule
The proposed rule on the ``Treatment of Data Influenced by
Exceptional Events'' was issued on March 10, 2006 (71 FR 12592). We
received 98 letters from commenters representing 587 comments from
private citizens, State and local governments, industry, environmental
groups, and Federal agencies. Sections V, VI, VII, and VIII of this
notice describe the primary elements and requirements concerning the
process for the handling of data influenced by exceptional events. Each
section summarizes the relevant issues and options discussed in the
proposed rule and provides the final decisions related to the issues
for each section. In this preamble, we have provided responses to
certain significant comments to elaborate or provide clarification for
EPA's decision on an issue discussed in the relevant section of the
rule. We have developed a response to comments document which addresses
all of the timely comments received on the proposed rule. Following the
promulgation of this rule, the response to comments document will be
placed into the docket of this rulemaking action for public review (See
Docket No. EPA-HQ-OAR-2005-0159).
D. What Is an Exceptional Event?
In accordance with the language in section 319, EPA is defining 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 EPA 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 the purposes of this rule,
EPA is defining ``natural event'' as an event in which human activity
plays little or no direct causal role 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 adopting section 188(f) of part D, subpart 4, of the 1990 amendments
to
[[Page 13564]]
the CAA, Congress recognized and provided for distinctions between
these types of events with respect to waiver of applicable requirements
and the extension of otherwise applicable attainment dates for the
PM10 standard. In approving section 188(f) of the CAA, the
House committee of jurisdiction discussed a circumstance in which
recurring emissions from a source should be considered to be
anthropogenic. The House report noted EPA statements that, in the cited
case, high concentrations of dust from a lakebed were due to human
activity, i.e., the long-term diversion of water from a lake. (See Pub.
L. 101-549, CAA Amendments of 1990 House Report No. 101-290(l), May 17,
1990; and discussion of Mono Lake, California therein). Also, EPA
recognized, in recently acting to retain PM10 as a measure
of coarse particulate, that in some instances exceedances of this NAAQS
``may be caused in whole or in part, by exceptional events, including
natural events such as windstorms * * *. (and that) an exceedance may
be treated as an exceptional event even though anthropogenic sources
such as agricultural and mining emissions contribute to the
exceedance.'' (71 FR 61216; October 17, 2006).
In this final 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 finalizing 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.
E. 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 rule provided that all other requirements of the
rule are met. By providing the examples listed below, EPA is not
determining that such events are the only types of events that may
qualify for exclusion under the rule as exceptional events. Other
events that meet the statutory criteria for an exceptional event as
defined in this rule may also qualify for exclusion. The AQS user
documentation contains a list of other similar events that may be
flagged for special consideration. (https://www.epa.gov/ttn/airs/
airsaqs/manuals/qualifiers.htm).\10\
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\10\ The EPA will be revising the list of events contained in
the AQS database following the promulgation of this rule to ensure
that the list is consistent with the requirements of the rule.
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In addition, in the sections below, we have provided responses to
certain significant comments received during the comment period for the
proposed rule regarding the examples of events that may meet the
definition of an exceptional event in order to elaborate upon or
provide clarification about what constitutes an exceptional event.
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.
Comments and Responses
Comment: Several commenters stated that ``Chemical Spills and
Industrial Accidents'' should generally not be considered exceptional
events. Commenters stated that most industrial accidents and chemical
spills are reasonably controllable and preventable with proper planning
and mitigation efforts. These commenters stated that allowing for
accidents or spills that could have been avoided is inconsistent with
the CAA.
Response: It is EPA's belief that air quality data that has been
affected by emissions from chemical spills, industrial accidents, or
structural fires may be flagged by a State as an exceptional event and
reviewed by EPA for exclusion on a case-by-case basis to determine
whether it meets the criteria for exceptional events as defined in this
rule. In particular, data influenced by chemical spills or industrial
accidents must be demonstrated to have ``affected air quality'' and
must be demonstrated to be due to circumstances that were not
reasonably controllable or preventable and are events that are unlikely
to recur in a particular location. The EPA agrees with the commenters
that industrial or point source emissions due to malfunctions or non-
compliance would not be considered exceptional events and should be
addressed through the normal State Implementation Planning process.
2. Structural Fires
Structural fires include any accidental fire involving a manmade
structure.
Comments and Responses
Comment: Several commenters indicated that ``Structural Fires''
should generally not be considered exceptional events. Commenters
stated that these types of events should be considered as emissions
from anthropogenic sources and handled within the form of the
respective air quality standards where a certain number of exceedances
of the standards are allowed over a 3-year period. Commenters assert
that structural fires, lasting for several hours, are unlikely to cause
an area to reach the level of nonattainment. In cases where structural
fires are determined to be the cause of a monitored violation of the
NAAQS, commenters stated that EPA should adopt a case-by-case review of
these events.
Response: The definition of structural fires under this rule
pertains to any accidental fire involving a manmade structure. The EPA
believes that structural fires could be an exceptional event under this
rule, provided all other requirements of the rule are met, because they
could ``affect air quality,'' could be an event that is not
``reasonably controllable'' or ``preventable,'' and could be events
that are caused by human activity that are unlikely to recur at the
same location. However, EPA agrees with the commenters that these types
of events, as well as other similar types of events, should be reviewed
on a case-by-case basis to determine whether they meet the criteria for
an exceptional event as defined by this rule.
3. Exceedances Due to Transported Pollution
Transported pollution, whether national or international in origin,
and whether from natural or anthropogenic sources, may cause
exceedances eligible for exclusion under this rule, as long as all of
the criteria and requirements related to exceptional events are met as
defined in this rule. 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 in an
area, leading to exceedances or violations of a NAAQS. An example of
interstate transported emissions which may be flagged as due to an
exceptional event would be emissions due to smoke from wildfires or
wildland fire use fires which cause exceedances or violations of the
NAAQS at monitoring sites in other States. Other examples could include
data affected by emissions from mining and agricultural activities when
such emissions are subjected to long-range transport, and the criteria
and
[[Page 13565]]
requirements related to an exceptional event are met as defined in this
rule. In general, events due to transported pollution may be considered
on a case-by-case basis.
Comments and Responses
Comment: Several commenters expressed concern over EPA allowing the
exceptional events rule to be used to exclude data that has been
affected by emissions emanating from sources outside the borders of the
United States.
Response: States may flag data that has been affected by sources
emanating from outside the United States that meet the criteria for an
exceptional event as defined under this rule, including requirements
for causation and documentation. In cases where an area is impacted by
emissions from sources outside of the United States which do not meet
the criteria for an exceptional event under this rule, and these
emissions contribute to an area being designated as nonattainment, the
emissions may be addressed under section 179B of the CAA related to
``International Border Areas.'' Section 179B provides that where a
State is required to submit a State Implementation Plan (SIP) to
address issues related to a nonattainment designation, EPA may approve
the SIP for the area provided that the plan (1) meets all the
applicable requirements called for under the CAA, other than the
requirement that the plan demonstrate attainment or maintenance of the
NAAQS, and (2) the SIP must demonstrate that the affected area would be
able to attain the standard by the applicable attainment date ``but
for'' emissions emanating from outside the United States.
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.
Comments and Responses
No comments were received on this topic.
5. Natural Events
The natural events addressed by this final rule are: (1) Natural
disasters and associated cleanup activities; (2) volcanic and seismic
activities; (3) high wind events; (4) wildfires and wildland fire use
fires; and (5) stratospheric ozone intrusions. The EPA will consider
other types of natural events on a case-by-case basis.
a. Natural Disasters and Associated Clean-Up Activities
For the purpose of flagging, major natural disasters such as
hurricanes and tornadoes for which State, local, or Federal relief has
been granted, and clean-up activities associated with these events, may
be considered exceptional events. The EPA believes that for a major
natural disaster, a timeframe up to 12 months is a reasonable time
period to allow for clean-up activities associated with these types of
activities. In cases where the damage caused by the event is so
substantial that a 12-month period is inadequate to address the clean
up that is necessary, a State may submit a request to EPA for an
extension of the 12-month time period. The EPA will grant requests for
extensions of the time period related to such events on a case-by-case
basis if the States submit adequate supporting information concerning
the reason for the extension as well as the length of time being
requested for the extension.
Comments and Responses
Comment: Several commenters indicated that EPA should limit the
time period associated with clean-up activities due to a natural
disaster. One commenter indicated that the exceptional events rule as
proposed would allow States to apply the term ``natural disaster'' very
broadly to include circumstances that would circumvent the intent of
the CAA. For example, declaring an episode of high summer temperatures
to be a natural disaster could potentially allow a State to exclude
high ozone levels which commonly occur during hot weather.
Response: A time period up to 12 months for clean-up activities is
permitted for major natural disasters, such as hurricanes and
tornadoes, for which State, local, or Federal relief has been granted,
may be flagged for exclusion as exceptional events under this rule. The
clean-up activities associated with these types of events may also be
flagged for exclusion as being due to an exceptional event. Given the
nature of a major natural disaster, the 12-month time period allowed
for clean-up activities following such disaster is a reasonable time
period, and is consistent with the time period being allowed for
volcanic and seismic activities under this rule. The period of high
summer temperatures noted in the comment would not represent a major
natural disaster, as described above, subject to the 12-month clean-up
period.
b. Volcanic and Seismic Activities
Ambient concentrations of particulate matter for which volcanic or
seismic activity caused or significantly contributed to high levels of
particulate matter in an affected area will be treated as natural
events. While generally 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
activities can contribute to ambient concentrations in several ways: it
may influence concentrations of particulate matter 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
which may lead to exceedances or violations of the NAAQS.
Comments and Responses
Comment: Several commenters indicated that the rule should provide
sufficient flexibility for data to be excluded where the duration of
the event may last for a long period of time. An example of such an
event is where volcanic activities last for several days.
Response: The EPA agrees with the commenters and notes that the
rule allows for States to flag data and submit documentation related to
events such as long-term volcanic and seismic activities. States may
also submit requests to EPA to extend the time period up to 12 months
for major natural disasters, for clean-up activities following volcanic
and seismic events. States are encouraged to submit supporting
information related to the reasons for the requested extension and the
length of time being requested for the extension.
c. High Wind Events
High wind events are events that affect ambient particulate matter
concentrations through the raising of dust or through the re-
entrainment of material that has been deposited. In some locations,
concentrations of coarse particles like PM10 are most likely
affected by these types of events, although PM2.5 standards
may be exceeded under such circumstances as well. Section VII.B. also
includes a discussion of this issue.
Comments and Responses
Comment: Several commenters suggested that EPA replace the term
[[Page 13566]]
``high winds'' with the term ``wind-generated dust'' because (1) it
places the emphasis on the natural mechanism, (2) dust may become
entrained at relatively low wind velocities, and (3) the change will
eliminate confusion between the wind speeds associated with a natural
event and wind speeds needed to qualify for a ``high wind'' exceptional
event under EPA's 1986 guidance.
Response: The EPA is retaining the term ``high wind'' event because
it accurately connotes the type of natural event that should be
excluded under this rule, as well as the action which caused the
exceedance or violation of the standard. The term also serves as an
indicator concerning the level of wind which caused the exceedance or
violation of the standard and indicates that it was unusually high for
the affected area during the time period that the event occurred.
Therefore, States must provide appropriate documentation to
substantiate why the level of wind speed associated with the event in
question should be considered unusual for the affected area during the
time of year that the event occurred. The EPA will evaluate such
instances on a case-by-case basis, including factors such as
historically typical windspeed levels for the season of the year that
the event is claimed.\11\
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\11\ As described elsewhere in the preamble, EPA is adopting a
weight of evidence approach to demonstrate that an exceptional event
caused an exceedance or violation. Therefore, in instances where the
level of the wind speed results in exceedances or violations of
particulate matter, for data affected by these events to be
considered for exclusion under the weight of evidence approach, a
clear causal relationship must be demonstrated between the
exceedances measured at the air quality monitoring site and the high
wind event in question. EPA will consider in the weight of evidence
analysis winds that produce emissions contributed to by
anthropogenic activities that have been controlled to the extent
possible through use of all reasonably available reasonable and
appropriate measures.
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d. Wildland Fires
Federal land managers have afforded recognition to several
different types of wildland fires (i.e., wildfire, wildland fire use
fire and prescribed fire), depending on their causal circumstances and
the role that such fires play in the affected ecosystems. Prescribed
fire is addressed more fully in the following section.
The question of what is a natural versus an anthropogenic fire has
particular significance when considering the impacts of wildland fires
(wildfire, wildland fire use fire and prescribed fire) on air quality
and how these impacts should be regarded under this rule. A
``wildfire'' is defined as an unplanned, unwanted wildland fire (such
as a fire caused by lightning), and include unauthorized human-caused
fires (such as arson or acts of carelessness by campers), escaped
prescribed fire projects (escaped control due to unforeseen
circumstances), where the appropriate management response includes the
objective to suppress the fire. In contrast, a ``wildland fire use''
fire is the application of the appropriate management response to a
naturally-ignited (e.g., as the result of lightning) wildland fire to
accomplish specific resource management objectives in predefined and
designated areas where fire is necessary and outlined in fire
management or land management plans.
Using these definitions, we believe that both wildfires and
wildland fire use fires fall within the meaning of ``natural events''
as that term is used in section 319. Therefore, ambient particulate
matter and ozone concentrations due to smoke from a wildland fire will
be considered for treatment as an exceptional event if the fire is
determined to be either a wildfire or wildland fire use fire.
Comments and Responses
Comment: In general, commenters strongly supported exempting
wildfires as exceptional events under the rule.
Response: The EPA acknowledges support for the proposal to classify
wildfires as a potential exceptional event. As noted above, the Agency
states that wildland fires will be excluded as exceptional events if
they meet the criteria and requirements of the exceptional events rule.
Comment: The Agency received comments both supporting and opposing
the proposal allowing wildland fire use fires to qualify as an
exceptional event.
Response: After reviewing Congress' revisions to section 319, the
various Agency policies cited in the proposal, and comments received,
the Agency has determined that wildland fire use fires may also qualify
as an exceptional event. However, these types of fires must also meet
certain criteria. For example, these fires must occur on lands that
have been designated in fire management or land management plans as
areas where fires are necessary and desirable to accomplish specific
resource management objectives.
Comment: Many commenters supported EPA's commitment to update the
1998 Interim Air Quality Policy on Wildland and Prescribed Fires to be
consistent with this rule.
Response: The Agency plans to begin revising this policy in 2007 as
part of its overall Fire Strategy after promulgation of this rule.
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 transported 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.
Comments and Responses
Comment: One commenter stated that EPA should update its approach
to stratospheric events, establish criteria by which such events may be
determined, and credit States for the impact of intrusion events on
non-compliant ozone monitor readings.
Response: Stratospheric ozone intrusion is identified as a natural
event under 40 CFR part 50, appendix I, for ozone, and will be
considered for treatment as an exceptional event.
6. Prescribed Fire
A ``prescribed fire'' is defined as any fire ignited by management
actions to meet specific resource management objectives. According to
existing Federal policy, prior to ignition a prescribed fire must have
an approved prescribed fire plan and must meet the National
Environmental Policy Act (NEPA) requirements (where applicable)(see
National Wildland Fire Coordination Group Glossary of Wildland Fire
Terminology, 2003). For purposes of section 319, a prescribed fire
cannot be classified as ``natural,'' given the extent of the direct
human causal connection, however, a prescribed fire may meet the
statutory criteria defined in section 319 of ``affect[ing] air
quality,'' being ``unlikely to recur at a particular location'' and is
``not reasonably controllable or preventable.'' The determination of
whether a prescribed fire can be considered an exceptional event should
be made on a case-by-case basis taking into account the factors
described below.
A prescribed fire carried out for resource management objectives is
frequently designed to restore essential ecological processes of fire
and mimic fire under natural conditions. As such, a prescribed fire's
expected frequency can vary widely, depending on the natural fire
return interval of a particular landscape or wildland ecosystem. The
natural fire return
[[Page 13567]]
interval can range from once every year to less frequently than once in
more than 200 years. Thus, in many, though not all cases, it may be
possible to demonstrate that the likelihood of recurrence is
sufficiently small enough to show that a prescribed fire under these
conditions meets the ``unlikely to recur at a particular location''
requirement of the statutory language.
A prescribed fire may also meet the condition of ``not reasonably
controllable or preventable'' by examining whether there are 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 significant build-up of
forest fuels in a particular area that if left unaddressed would pose
an unacceptable risk of catastrophic wildfire, which could result in
adverse impacts of much greater magnitude, duration, and severity than
would result from careful use of prescribed fire. A particular
ecosystem may also be highly dependent on a natural fire return
interval 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 prescribed 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 prescribed fire qualifies as being ``not reasonably controllable
or preventable.'' Thus, we believe that a prescribed fire, conducted by
Federal, State, Tribal or private wildland managers or owners, under
the conditions described above may qualify as an exceptional event.
In addition, one of the principles contained in SAFE-TEA-LU,
section 6013(b)(3)(A), includes the principle that States must take
necessary measures to safeguard public health regardless of the source
of air pollution. We believe it reasonable to tie the qualifying
criteria for an anthropogenically generated prescribed fire to State
accountability for public health protection. Consistent with historical
practice governed by the guidance contained in the ``Interim Air
Quality Policy on Wildland and Prescribed Fires,'' issued on May 15,
1998, EPA approval of exceedances linked to a prescribed fire used for
resource management purposes is contingent on the State certifying that
it has adopted and is implementing a Smoke Management Program (SMP) as
described in that policy. A State SMP establishes a basic framework of
procedures and requirements for managing smoke from a prescribed fire
managed for resource benefits. A SMP is typically developed by a State
or Tribe with cooperation and participation by wildland managers, both
public and private, and the general public. As reflected in the Interim
Air Quality Policy on Wildland and Prescribed Fires, States are
provided flexibility on the structure of a SMP. Thus, a SMP can be
extensive and detailed, or simply identify the basic smoke management
practices for minimizing emissions, and controlling impacts from a
prescribed fire.\12\ In the proposal to this rule, EPA proposed to
continue the use of that approach. We also proposed to expand the
criteria for contingent approval to a prescribed fire where, in lieu of
a SMP, basic smoke management practices, that minimize emissions and
control impacts, are being employed by burners. In order to protect
public health in areas where a SMP has not been adopted, in the final
rule, the Agency has elected to expand, on a case-by-case basis, the
qualifying criteria by which a prescribed fire may qualify as an
exceptional event. In those cases, the Agency will judge on a case-by-
case basis whether the State has ensured that appropriate basic smoke
management practices have been employed in determining whether the
prescribed fire qualifies as an exceptional event. If an exceptional
event occurs using the basic smoke management practices approach, the
State must undertake a review of their approach to ensure public health
is being protected and must include consideration of development of a
SMP.
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\12\ Basic smoke management practices could include, among other
practices, steps that will minimize air pollutant emissions during
and after the burn, evaluate dispersion conditions to minimize
exposure of sensitive populations, actions to notify populations and
authorities at sensitive receptors and contingency actions during
the fire to reduce exposure of people at such receptors, identify
steps taken to monitor the effects of the fire on air quality, and
identify procedures to ensure that burners are using basic smoke
management practices.
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Comments and Responses
Comment: Several commenters supported classifying prescribed fire
as qualifying as an exceptional event. However, some commenters
indicated that there should be limitations placed on when this type of
fire should be considered as an exceptional event. A number of
commenters also disapproved of allowing prescribed fire to be
considered as an exceptional event because they believe that this type
of fire is anthropogenic and does not meet the statutory definition of
exceptional event. Some commenters also favored expanding the criteria
for contingent approval to include instances where basic smoke
management practices are used in lieu of a SMP, while other commenters
did not favor this expansion.
Response: The EPA believes that a prescribed fire may be excluded
as an exceptional event under this rule only in cases where the event
meets the criteria for an exceptional event as defined in this rule, if
documentation is submitted to show that the fire meets the requirement,
as described above, of ``affect[ing] air quality,'' being ``not
reasonably controllable or preventable'' and ``unlikely to recur at
location'' and provided the other requirements of the rule including,
among others, the schedules and procedures for flagging and
demonstration are met. In those instances where a prescribed fire meets
the criteria for an exceptional event, the State must also provide
appropriate documentation to show that a certified SMP was in place or
that the burner employed basic smoke management practices and that the
appropriate practices were being followed at the time that the event
occurred. Because a prescribed fire is an anthropogenic source of
emissions for purposes of section 319, even though it may qualify as an
exceptional event, a State can attempt to limit the health impact of a
prescribed fire through the thoughtful development and implementation
of a SMP or ensuring that basic smoke management practices were
employed that minimize emissions and control impacts from prescribed
fires.
V. The Management of Air Quality Data Affected by Exceptional Events
The EPA proposed that, in order to exclude air quality data from
consideration for regulatory purposes, States must follow the
procedures, timelines, and other requirements described in the proposed
rule. Under the Final Rule, if an event is determined to be a
qualifying exceptional event according to section IV.D, a State, Tribe,
or designated local agency may petition EPA to classify the event as
exceptional and submit a demonstration to justify data exclusion.\13\
For data exclusion, States must clearly identify, or ``flag,''
[[Page 13568]]
data they believe to be influenced by such events. The demonstration to
justify data exclusion shall provide evidence that: (a) The event
qualifies in accordance with section IV.D and with EPA policies and
guidance for certain events as described in section IV.E, (b) there is
a clear causal relationship between the measurement under consideration
and the event that is claimed to have affected the air quality in the
area, (c) the event is associated with an unusual measured
concentration beyond typical fluctuations including background, and (d)
that there would have been no exceedance or violation but for the
event.
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\13\ Although a single qualifying exceptional event may affect
air quality for multiple days and at multiple monitors, the
discussions below consider an individual demonstration as justifying
exclusion of a single AQS data point. The EPA encourages State
submittals to package demonstrations about single exceptional events
to expedite the review process.
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The SAFE-TEA-LU requirements for exclusion of data from exceptional
events are: (1) The occurrence of the exceptional event must be
demonstrated by reliable and accurate data; (2) the State must show
that there is a ``clear causal relationship'' between the NAAQS
exceedances and the event; (3) there must be a public review process
related to the exceptional event determination; and (4) the rule must
set criteria and procedures for States to petition EPA to exclude data
directly affected by an exceptional event. The sections below describe
how each of these requirements must be met.
The sections below address the flagging of data as exceptional
events that are determined to have affected air quality, submittal of
demonstrations to request data exclusion, public review, and the
schedule and timing for these processes. After an exceptional event
occurs (judged according to section IV.D) and an agency determines that
the event affected ambient air quality, flagging may occur according to
section V.A. Section V.B describes the evaluation of whether or not the
event affected ambient air quality. Section V.C describes the necessary
``but-for'' test that data would have complied with the applicable
standard but for the occurrence of the exceptional event. Section V.D
explains the schedules and procedures for the flagging and
demonstration submittals, section V.E discusses the applicability to
hourly readings, section V.F states the requirements for determination
submittals if the agency requests EPA to exclude the data from
consideration for regulatory purposes, and section V.G describes the
public review requirements. Some commenters suggested that all data
occurring from exceptional events should be flagged, and EPA will allow
these flags for informational purposes, even if the data do not qualify
for exclusion. If EPA concurs on the exclusion of data from qualifying
exceptional events, the data will be excluded from regulatory
consideration but will still count toward data capture requirements.
A. Flagging of Data in the AQS Database
1. Background
Air quality data are required, pursuant to 40 CFR 58.16, 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 submitte