Proposed Implementation Requirements for Reduction of Sulfur Oxide (Sulfur Dioxide) Emissions
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Federal Register › Vol. 62 › 62 FR 210
Text
Part IV
Environmental Protection Agency
_______________________________________________________________________
40 CFR Part 51
Proposed Implementation Requirements for Reduction of Sulfur Oxide
(Sulfur Dioxide) Emissions; Proposed Rule
Proposed Rules
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 51
[AD-FRL-5670-8]
RIN 2060-AA61
Proposed Implementation Requirements for Reduction of Sulfur
Oxide (Sulfur Dioxide) Emissions
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
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SUMMARY: The EPA is proposing a new intervention level program under
the authority of sections 301(a)(1) and 303 of the Clean Air Act (Act)
to supplement protection provided by the primary and secondary sulfur
dioxide (SO2) national ambient air quality standards (NAAQS). The
program proposed today is in lieu of the three alternative
implementation strategies for reducing high 5-minute SO2
concentrations in the ambient air proposed on March 7, 1995.
The intervention level program addresses EPA's concern that a
segment of the asthmatic population may be at increased health risk
when exposed to 5-minute peak concentrations of SO2 in the ambient
air while exercising (``exercising'' in this case can include walking
up stairs or hills, as well as more strenuous activities). At certain
concentration levels or frequencies, such peaks can represent imminent
and substantial endangerment to public health. This proposed program
also responds to comments received on the March 7, 1995 proposal.
In addition, EPA is reproposing the implementation strategy for
identifying and prioritizing areas with potential 5-minute SO2
peaks. The changes to the monitoring strategy discussed in the March 7,
1995 proposal address public comments regarding the flexibility of the
strategy and the criteria used to identify sources for monitoring
esponds to comments received on the March 7, 1995 proposal.
In addition, EPA is reproposing the implementation strategy for
identifying and prioritizing areas with potential 5-minute SO2
peaks. The changes to the monitoring strategy discussed in the March 7,
1995 proposal address public comments regarding the flexibility of the
strategy and the criteria used to identify sources for monitoring.
Finally, EPA has reviewed comments concerning the revisions to the
24-hour significant harm levels (SHL) for SO2 discussed in the
March 7, 1995 proposal. After further consideration, the EPA now
believes the proposed revisions to those levels are not needed at this
time. The EPA is requesting comment on whether the proposed changes to
the SHL are necessary or should be withdrawn.
DATES: Written comments on this proposal must be received by March 3,
1997. Persons wishing to present oral testimony pertaining to this
notice should contact EPA at the address listed below under FOR FURTHER
INFORMATION CONTACT by January 17, 1997. If anyone contacts EPA
requesting to speak at a public hearing, a separate notice will be
published announcing the date, time, and place where the hearing will
be held.
ADDRESSES: Submit comments on this proposal (two copies are preferred)
to: Office of Air and Radiation Docket and Information Center (Air
Docket 6102), Room M 1500, U.S. Environmental Protection Agency,
Attention: Docket No. A-94-55, 401 M Street, SW, Washington, DC 20460.
The docket may be inspected between 8:00 a.m. and 5:30 p.m. on
weekdays, and a reasonable fee may be charged for copying. The Air
Docket may be called at (202) 260-7548. For the availability of related
information, see SUPPLEMENTARY INFORMATION.
FOR FURTHER INFORMATION CONTACT: Eric L. Crump, Integrated Policies and
Strategies Group (MD-15), U.S. Environmental Protection Agency,
Research Triangle Park, NC 27711, telephone (919) 541-4719.
SUPPLEMENTARY INFORMATION:
Regulated Entities
may be charged for copying. The Air
Docket may be called at (202) 260-7548. For the availability of related
information, see SUPPLEMENTARY INFORMATION.
FOR FURTHER INFORMATION CONTACT: Eric L. Crump, Integrated Policies and
Strategies Group (MD-15), U.S. Environmental Protection Agency,
Research Triangle Park, NC 27711, telephone (919) 541-4719.
SUPPLEMENTARY INFORMATION:
Regulated Entities
Entities potentially regulated by this action are those which
contribute to 5-minute ambient SO2 concentrations that pose a
health threat to sensitive, exposed populations. Regulated categories
and entities would include:
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Category Examples of regulated entities
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Industry..................... Pulp and paper mills, lead, aluminum, and
copper smelters, petroleum refineries,
iron and steel mills, carbon black
manufacturers, portland cement plants,
oil and gas extraction processes,
fertilizer manufacturers, industrial and
utility boilers, sulfuric acid plants.
Federal government........... Federal agencies which operate industrial
or utility boilers.
State/tribal government...... State/tribal agencies which operate
industrial or utility boilers.
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This table is not intended to be exhaustive; furthermore, entities
listed in this table would not necessarily be subject to regulation
under this proposed action. This table is intended only as a guide for
readers regarding entities likely to be regulated by this action. This
table lists the types of entities that EPA believes could potentially
be regulated by this action. Other types of entities not listed in the
table could also be regulated
ore, entities
listed in this table would not necessarily be subject to regulation
under this proposed action. This table is intended only as a guide for
readers regarding entities likely to be regulated by this action. This
table lists the types of entities that EPA believes could potentially
be regulated by this action. Other types of entities not listed in the
table could also be regulated. To determine whether your facility,
company, business or organization would be regulated by this proposed
action, you should ascertain whether your facility, company, business,
or organization (1) emits SO2, and (2) is located in an area
subject to ambient air concentrations that exceed the criteria in
Sec. 51.154 of 40 CFR. If you have questions regarding the
applicability of this action to a particular entity, consult the person
listed in the preceding FOR FURTHER INFORMATION CONTACT section.
Availability of Related Information.
The 1982 revised criteria document, Air Quality Criteria for
Particulate Matter and Sulfur Oxides (three volumes, EPA-600/8-82-
029af-cf, December 1982; Volume I, NTIS # PB-84-120401, $36.50 paper
copy and $9.00 microfiche; Volume II, NTIS # PB-84-120419, $77.00 paper
copy and $9.00 microfiche; Volume III, NTIS # PB-84-120427, $77.00
paper copy and $20.50 microfiche); the 1986 criteria document addendum,
Second Addendum to Air Quality Criteria for Particulate Matter and
Sulfur Oxides (1982): Assessment of Newly Available Health Effects
Information (EPA/600/8-86-020-F, NTIS # PB-87-176574, $36.50 paper copy
and $9.00 microfiche); the 1994 criteria document supplement,
Supplement to the Second Addendum (1986) to Air Quality Criteria for
Particulate Matter and Sulfur Oxides (1982): Assessment of New Findings
on Sulfur Dioxide Acute Exposure Health Effects in Asthmatic
Individuals (1994) (EPA-600/FP-93/002); the 1982 staff paper, Review of
the National Ambient Air Quality Standards for Sulfur Oxides:
Assessment of Scientific and Technical Information (EPA-450/5-82-007,
No
the Second Addendum (1986) to Air Quality Criteria for
Particulate Matter and Sulfur Oxides (1982): Assessment of New Findings
on Sulfur Dioxide Acute Exposure Health Effects in Asthmatic
Individuals (1994) (EPA-600/FP-93/002); the 1982 staff paper, Review of
the National Ambient Air Quality Standards for Sulfur Oxides:
Assessment of Scientific and Technical Information (EPA-450/5-82-007,
November 1982; NTIS # PB-84-102920, $36.50 paper copy and $9.00
microfiche); the 1986 staff paper addendum, Review of the National
Ambient Air Quality Standards for Sulfur Oxides: Updated Assessment of
Scientific and Technical Information (EPA-450/05-86-013, December 1986;
NTIS # PB-87-200259, $19.50 paper copy and $9.00 microfiche) and the
1994 staff paper supplement, Review of the National Ambient Air Quality
Standards For Sulfur Oxides: Updated Assessment of Scientific and
Technical Information, Supplement to the 1986 OAQPS Staff Paper
Addendum (1994) (EPA-452/R-94-013, September 1994; NTIS # PB-95-124160,
$27.00 paper copy and $12.50 microfiche) are available from: U.S.
Department of Commerce, National Technical Information Service, 5285
Port Royal Road, Springfield, Virginia 22161, or call 1-800-553-NTIS.
(Add $3.00 handling charge per order.)
Table of Contents
I. Background
A. Overview
B. Rulemaking Docket
II. Intervention Level Program
A. Program Highlights
B. Health Effects and Basis for Levels
C. Flexible Implementation Strategy
III. Legal Authority
IV. Program Implementation
A. Requirements Associated with the Implementation of the
Intervention Level Program
B. Compliance and Enforcement Issues
V. Relationship Between the Intervention Level Program and Existing
Programs
A. Impact on SIPs, Attainment Planning and Implementation
B. Malfunctions
C. Significant Harm Level Program
D. Acid Rain Program
VI. Community Involvement in the Intervention Level Program
VII. Source Prioritization and Monitor Allocation
VIII
n of the
Intervention Level Program
B. Compliance and Enforcement Issues
V. Relationship Between the Intervention Level Program and Existing
Programs
A. Impact on SIPs, Attainment Planning and Implementation
B. Malfunctions
C. Significant Harm Level Program
D. Acid Rain Program
VI. Community Involvement in the Intervention Level Program
VII. Source Prioritization and Monitor Allocation
VIII. Reconsideration of Proposed 24-Hour Significant Harm Level and
Episodes Criteria
IX. Comments and the Public Docket
X. Administrative Requirements
A. Executive Order 12866
B. Monitoring and Administrative Costs
C. Regulatory Flexibility Analysis
D. Impact on Reporting Requirements
E. Unfunded Mandates Reform Act
F. Environmental Justice
References
SUPPLEMENTARY INFORMATION:
I. Background
A. Overview
As discussed in the November 15, 1994 proposal (59 FR 58958), EPA
completed a thorough review of the air quality criteria and the current
SO2 NAAQS required by sections 108 and 109 of the Act and
concluded provisionally that the current 24-hour and annual primary
standards provide adequate protection against the effects associated
with those averaging periods. The key issue that emerged from the
review is whether additional regulatory measures are needed to provide
additional protection for asthmatic individuals that may be exposed to
high 5-minute peak SO2 concentrations.
As explained in the March 7, 1995 Federal Register proposal (60 FR
12492), the available air quality and exposure data indicate that the
likelihood that the asthmatic population in general would be exposed to
5-minute peak SO2 concentrations of concern, while outdoors and at
exercise, is very low when viewed from a national perspective
may be exposed to
high 5-minute peak SO2 concentrations.
As explained in the March 7, 1995 Federal Register proposal (60 FR
12492), the available air quality and exposure data indicate that the
likelihood that the asthmatic population in general would be exposed to
5-minute peak SO2 concentrations of concern, while outdoors and at
exercise, is very low when viewed from a national perspective. The data
indicate, however, that high peak SO2 concentrations can occur
around certain sources with some frequency, and as a result, asthmatic
individuals in the vicinity of such sources would be subject to a
greater health risk than asthmatics not subject to such peaks or the
nonasthmatic population. These assessments lead EPA to believe that if
any additional regulatory measures are adopted to provide additional
protection, they should be addressed through an approach that focuses
on those locations where the sensitive population is more likely to be
exposed to high 5-minute peak SO2 concentrations.
Based on these considerations, EPA requested comment on three
regulatory measures proposed on March 7, 1995 to address high 5-minute
SO2 peaks: (1) augmenting implementation of the existing standards
by focusing on those sources or source types likely to produce high 5-
minute peak SO2 concentrations; (2) establishing a new regulatory
program under section 303 of the Act to supplement the protection
provided by the existing NAAQS; and (3) supplementing the existing
NAAQS with a 5-minute NAAQS of 0.60 parts per million (ppm).
The public comments received represented various concerns regarding
the three alternatives
es or source types likely to produce high 5-
minute peak SO2 concentrations; (2) establishing a new regulatory
program under section 303 of the Act to supplement the protection
provided by the existing NAAQS; and (3) supplementing the existing
NAAQS with a 5-minute NAAQS of 0.60 parts per million (ppm).
The public comments received represented various concerns regarding
the three alternatives. Of the many comments received, the following
arguments appeared to be most compelling: (1) short-term peak emissions
are more of a localized issue rather than a widespread concern and that
instead of a broad national regulatory program, States and tribes
should be given the authority to address such issues; and (2) States
and tribes need more flexibility to address situations that create
exposures to high short-term ambient concentrations, especially in
cases when the short-term peaks are rare and the potential for exposure
is low (for example, when the source is located in a relatively
isolated area). The comments received confirm EPA's original assessment
that high 5-minute peak episodes of SO2 are not a uniformly
widespread problem; rather, these episodes are limited to certain
localized areas throughout the country. The EPA now believes that a
national regulatory program developed for implementation by every State
and tribe would be counterproductive, placing an administrative burden
on many parts of the country that are not subject to risk from these
peak concentrations.
Although these episodes are few, it is clear that 5-minute SO2
ambient concentration peaks pose a health threat to sensitive, exposed
populations, and that the severity of the threat depends upon the
concentration and frequency of peak episodes and the size of the
population subject to the peak episodes
on many parts of the country that are not subject to risk from these
peak concentrations.
Although these episodes are few, it is clear that 5-minute SO2
ambient concentration peaks pose a health threat to sensitive, exposed
populations, and that the severity of the threat depends upon the
concentration and frequency of peak episodes and the size of the
population subject to the peak episodes. Because every area that is
subject to significant short-term peaks has its own unique
characteristics, EPA agrees it is prudent for States, local
governments, and tribal governments to assess each individual
situation, and if a significant threat to public health exists, act
appropriately and efficiently to reduce the risk to the public. The EPA
wishes to establish an implementation program that (1) effectively
addresses real health concerns, (2) provides States, tribes, and local
communities with a basis for taking protective action, and (3) provides
flexibility to address a given situation appropriately.
For the reasons discussed in the May 22, 1996 Federal Register
final decision (61 FR 25566), EPA has concluded that revisions to the
existing SO2 NAAQS are not appropriate at this time. In lieu of
the three alternative approaches originally proposed to address 5-
minute concentrations, EPA now proposes an intervention level program
under the authority of section 303 of the Act to address the risk
presented by 5-minute SO2 concentrations.
Because health effects caused by 5-minute SO2 ambient
concentrations tend to be localized problems, EPA believes the
intervention level program is the appropriate approach to address this
concern. Instead of a uniform nationwide approach that might call for
unnecessary administrative effort, this program would allow placement
of resources and efforts precisely where the problems are
rations.
Because health effects caused by 5-minute SO2 ambient
concentrations tend to be localized problems, EPA believes the
intervention level program is the appropriate approach to address this
concern. Instead of a uniform nationwide approach that might call for
unnecessary administrative effort, this program would allow placement
of resources and efforts precisely where the problems are. It would
allow States, tribes, and local governments to analyze the variable
issues relevant to peak concentration episodes in their jurisdiction,
giving them the flexibility to address the sources of the peak
emissions more efficiently and appropriately. The intervention level
program would also provide a catalyst for community-based approaches to
environmental protection by encouraging States and tribes to
incorporate citizen concerns and complaints into their criteria for
assessing public health risk.
B. Rulemaking Docket
Docket No. A-94-55 has been established for supporting
documentation for the action proposed today. The EPA established a
standard review docket (Docket No. A-79-28) for the sulfur oxides
review in July 1979. The EPA also established a rulemaking docket
(Docket No. A-84-25) for the April 26, 1988 proposal under section
307(d) of the Act. Docket No. A-84-25 was used for the most current
review of the SO2 NAAQS. Both of these dockets, as well as a
separate docket established for criteria document revision (Docket No.
ECAO-CD-79-1), are hereby incorporated into the rulemaking docket for
the action proposed today.
II. Intervention Level Program
A. Program Highlights
r the April 26, 1988 proposal under section
307(d) of the Act. Docket No. A-84-25 was used for the most current
review of the SO2 NAAQS. Both of these dockets, as well as a
separate docket established for criteria document revision (Docket No.
ECAO-CD-79-1), are hereby incorporated into the rulemaking docket for
the action proposed today.
II. Intervention Level Program
A. Program Highlights
The proposed intervention level program is derived in part from the
SHL program, which has served in the past as a means for implementing
the authority granted under section 303 of the Act. The SHL program was
designed to address emergency episodes that occur where pollution
levels build up over a period of time to unhealthy levels. The SHL
program establishes a specific pollutant concentration within a given
time period that is known to pose a significant threat to human health
and that would require specific measures on the part of the State or
tribe and emission sources to correct. In addition, the program
establishes several degrees or levels of response which are triggered
by pollutant concentrations below the SHL. As the concentration of a
pollutant rises to each level, emission sources in the area are
required to take increasingly restrictive action to reduce emissions as
specified in the contingency plan within an approved State
implementation plan (SIP). The SHL program is a proactive program
designed to prevent an area from ever reaching the SHL.
The EPA contemplated using a similar approach to address 5-minute
peak emissions of SO2, but believes the SHL program would not be
the best means for addressing such short term peak episodes. A 5-minute
ambient concentration peak encompasses a short period of time compared
to the 3-hour and 24-hour periods used in the SHL program
rogram
designed to prevent an area from ever reaching the SHL.
The EPA contemplated using a similar approach to address 5-minute
peak emissions of SO2, but believes the SHL program would not be
the best means for addressing such short term peak episodes. A 5-minute
ambient concentration peak encompasses a short period of time compared
to the 3-hour and 24-hour periods used in the SHL program. The EPA
believes it is impractical to expect industry, States, and tribes to
have a predetermined course of corrective action in place to stop 5-
minute peak episodes as they occur because 5-minute episodes would
generally be over before remedial action could be taken to stop them.
In the view of the Administrator, this situation calls for a more
reactive approach as opposed to the proactive approach called for in
the SHL program. The EPA believes that its authority under sections
301(a)(1) and 303 of the Act provides for the creation of a new program
to address these short term peaks of SO2--the intervention level
program.
The intervention level program proposed herein would be similar to
the SHL program in that it would establish concentration levels in the
CFR that provide a basis for action by States, tribes and industry if
those levels are reached. As a supplement to the four concentration
levels specified in the SHL program, EPA proposes a range of
concentrations under the intervention level program. The lower boundary
of this range would be the concern level, set at 0.60 ppm of SO2,
based on a 5-minute hourly maximum value (a 5-minute hourly maximum
value for SO2 is the highest of the 5-minute averages from the 12
possible nonoverlapping periods during a clock hour). The upper
boundary of this range would be the endangerment level, set at 2.0 ppm
of SO2, based on a 5-minute hourly maximum value
r boundary
of this range would be the concern level, set at 0.60 ppm of SO2,
based on a 5-minute hourly maximum value (a 5-minute hourly maximum
value for SO2 is the highest of the 5-minute averages from the 12
possible nonoverlapping periods during a clock hour). The upper
boundary of this range would be the endangerment level, set at 2.0 ppm
of SO2, based on a 5-minute hourly maximum value. These
intervention levels are based on the health criteria discussed below
and in the May 22, 1996 part 50 final action (61 FR 25566), and would
be used by States and tribes along with other factors to determine
whether occurrences of 5-minute SO2 concentrations require action
to address ``* * * imminent and substantial endangerment to public
health or welfare, or the environment * * *'', as stated in section 303
of the Act.
In the event that the concern level concentration is exceeded in a
given area, and the State or tribe has reason to believe that the
exceedance may constitute imminent and substantial endangerment, the
State or tribe would assess the situation to determine whether
intervention is appropriate. In making this determination, the State or
tribe would consider the magnitude of the 5-minute peak concentrations;
the frequency of the episodes (based on those episodes detected by
monitors and an estimate of the number of 5-minute peaks not recorded
by the monitoring network); the history and nature of citizen
complaints; available information on potential population exposure,
inferred in part by the population in the vicinity of the source; the
type of process being used (i.e., one type of process within a source
category may be less efficient and known to emit more SO2 than
another); the history of past upsets or malfunctions; the type of fuel
used; knowledge of how well the source is controlled; and any other
considerations the State or tribe finds to be appropriate
rred in part by the population in the vicinity of the source; the
type of process being used (i.e., one type of process within a source
category may be less efficient and known to emit more SO2 than
another); the history of past upsets or malfunctions; the type of fuel
used; knowledge of how well the source is controlled; and any other
considerations the State or tribe finds to be appropriate. Because the
health effects become more severe as the 5-minute SO2
concentration approaches the endangerment level, it is reasonable to
expect that the State or tribe would be more likely to determine that
intervention is warranted, and that the degree of intervention judged
to be necessary would increase. If the endangerment level is exceeded,
thereby exposing a significant population to imminent and substantial
endangerment, the State or tribe may consider taking immediate action
to protect public health. Even in cases when the endangerment level is
exceeded, it is conceivable that the State or tribe may determine that
no action is warranted. For example, if the exceedance is linked to an
unusual circumstance not likely to reoccur, or causes minimal impact on
public health, the State or tribe may conclude that corrective measures
are not needed at this time.
In general the State or tribe will assess the health risk and
implement corrective measures under the intervention level program, not
EPA. If necessary, EPA would take action under the authority of section
303, as appropriate, in the event that the State or tribe fails to
address (1) imminent and substantial endangerment to public health
presented by exceedances of the endangerment level, or (2) evidence
that exceedances above the concern level (but below the endangerment
level) cause imminent and substantial endangerment due to their
frequency, magnitude, and reported health impacts.
B. Health Effects and Basis for Levels
ent that the State or tribe fails to
address (1) imminent and substantial endangerment to public health
presented by exceedances of the endangerment level, or (2) evidence
that exceedances above the concern level (but below the endangerment
level) cause imminent and substantial endangerment due to their
frequency, magnitude, and reported health impacts.
B. Health Effects and Basis for Levels
The health effects associated with exposures to the concern level,
0.60 ppm SO2, 5-minute block average, were the focus of EPA's most
recent review of the primary NAAQS for sulfur oxides (measured as
sulfur dioxide). The health effects and the Administrator's conclusions
about the public health risks associated with exposure to the concern
level are thoroughly discussed in the EPA documents generated during
that review: the criteria document supplement (EPA, 1994a), the staff
paper supplement (EPA 1994b), the November 15, 1994 proposal (59 FR
58958) and the May 22, 1996 final decision on part 50 (61 FR 25566).
These documents are incorporated into today's proposal by reference.
The EPA's concern about the potential public health consequences of
exposures to short-term peaks of SO2 arose from the extensive
literature involving brief (2- to 10-min) controlled exposures of
persons with mild (and, in some cases moderate) asthma across the
ranges of concentrations of SO2 to greater than 2.0 ppm while at
elevated ventilation rates. The major effect of SO2 on sensitive
asthmatic individuals is bronchoconstriction, usually evidenced in
these studies by decreased lung function (i.e., decreased forced
expiratory volume in 1 second (FEV1) and increased specific airway
resistance (SRaw)) and the occurrence of clinical symptoms such as
wheezing, chest tightness, and shortness of breath. The proportion of
asthmatic individuals who respond, the magnitude of the response and
the occurrence of symptoms increase as SO2 concentrations and
ventilation rates increase
function (i.e., decreased forced
expiratory volume in 1 second (FEV1) and increased specific airway
resistance (SRaw)) and the occurrence of clinical symptoms such as
wheezing, chest tightness, and shortness of breath. The proportion of
asthmatic individuals who respond, the magnitude of the response and
the occurrence of symptoms increase as SO2 concentrations and
ventilation rates increase. The criteria document supplement (EPA,
1994a) contains a summary of the literature on the health effects
associated with brief exposures to SO2.
Taking into account the available health effects studies and the
body of comments on the health effects, the Administrator concluded in
the May 22, 1996 final decision (61 FR 25566) that a substantial
percentage (20 percent or more) of mild-to-moderate asthmatic
individuals exposed to 0.60 to 1.0 ppm SO2 for 5 to 10 minutes at
elevated ventilation rates, such as would be expected during moderate
exercise, would be expected to have lung function changes and severity
of respiratory symptoms that clearly exceed those experienced from
typical daily variation in lung function or in response to other
stimuli (e.g., moderate exercise or cold/dry air). The
bronchoconstriction caused by brief exposures to 0.6 to 1.0 ppm
SO2 is transient (i.e., measurements of lung function start to
improve when exposure ceases or when the individual ceases to exercise
and ventilation rates return to resting levels). However, for many
responders, the effects are likely to be both perceptible and thought
to be of some health concern; that is, likely to cause some disruption
of ongoing activities, use of bronchodilator medication, and/or
possibly seeking of medical attention.
During the regulatory review process, there was some agreement by
medical experts that at this concentration, 0.60 ppm SO2, the
frequency with which such effects are experienced may affect the degree
of public health risk
o be of some health concern; that is, likely to cause some disruption
of ongoing activities, use of bronchodilator medication, and/or
possibly seeking of medical attention.
During the regulatory review process, there was some agreement by
medical experts that at this concentration, 0.60 ppm SO2, the
frequency with which such effects are experienced may affect the degree
of public health risk. After taking into account the broad range of
opinions expressed by Clean Air Scientific Advisory Committee (CASAC)
members, medical experts, and the public in the part 50 final decision,
the Administrator concluded that repeated occurrences of such effects
should be regarded as significant from a public health standpoint.
Furthermore, the Administrator determined that the likely frequency of
occurrence of such effects should be a consideration in assessing the
overall public health risk in a given situation.
The available scientific literature indicates that in the range of
0.60 to 2.0 ppm SO2, there is a dose-response relationship between
SO2 concentration and (1) the magnitude of the lung function
changes, and (2) the proportion of the asthmatic individuals expected
to respond. At 1.0 ppm SO2, 5-minute block average, approximately
60 percent of the mild-to-moderate asthmatic individuals at elevated
ventilation rates are likely to respond. The health effects become more
pronounced, with more substantial changes in pulmonary function
accompanied by symptoms. Asthmatic individuals may experience mild
bronchoconstriction without symptoms while at rest (EPA, 1986a; EPA,
1986b).
At 2.0 ppm SO2, 5-minute block average, approximately 80
percent of mild-to-moderate asthmatic individuals at elevated
ventilation rates are likely to respond. Effects can range from
moderate to incapacitating. Asthmatic individuals at rest are likely to
experience moderate bronchoconstriction
ent (EPA, 1982a)
and the 1982 staff paper (EPA, 1982b). Based upon this information, EPA
believes that exposure of a sensitive population to a 5-minute ambient
concentration of 2.0 ppm or above would pose an imminent and
substantial endangerment to public health and welfare and, therefore,
would justify corrective action under the authority of section 303.
C. Flexible Implementation Strategy
Like the previously proposed implementation alternatives, a key
element of this new implementation strategy is the relocation of
existing SO2 monitors to areas near point sources where peak
SO2 concentrations may exist. Because the monitors in the existing
State and local area monitoring stations (SLAMS) network were designed
to characterize urban ambient air quality associated with 3-hour, 24-
hour, and annual SO2 concentrations, they are not always the
appropriate means for measuring 5-minute peak SO2 concentrations
from point sources. To make existing monitors available for the
measurement of short-term peak concentrations, EPA proposed certain
technical changes to the requirements for ambient air monitoring
reference and equivalent methods (40 CFR part 53) and revisions to the
ambient air quality surveillance requirements (40 CFR part 58) in the
November 15, 1994 (59 FR 58958) and the March 7, 1995 (60 FR 12492)
proposals, respectively.
The EPA believes these changes to the monitoring requirements will
give the States and tribes the flexibility to relocate existing
monitors to areas where 5-minute peak concentrations may be of concern,
and to respan the monitors to measure these peaks. Under the
intervention level program, the States and tribes would be able to
identify areas to be monitored based on State or tribal priorities,
source emissions, citizen complaints, location of sensitive
populations, or other variables
e flexibility to relocate existing
monitors to areas where 5-minute peak concentrations may be of concern,
and to respan the monitors to measure these peaks. Under the
intervention level program, the States and tribes would be able to
identify areas to be monitored based on State or tribal priorities,
source emissions, citizen complaints, location of sensitive
populations, or other variables. Upon request, EPA would assist State
and tribal efforts to identify and prioritize areas for monitoring 5-
minute peak concentrations by providing information compiled from
various databases. The EPA would leave the discretion on how best to
utilize this information in siting monitors to the States and tribes.
If the State or tribe has ample reason to believe that areas within its
jurisdiction do not experience health risks from 5-minute peak
concentrations (for example, no sources with significant compliance
issues, maintenance problems or upsets; no complaints about detrimental
health effects from short-term peak SO2 concentrations), the State
or tribe would be justified in not relocating SO2 monitors for
this purpose.
III. Legal Authority
In the November 15, 1994 Federal Register action (59 FR 58958), EPA
discussed the legal authority for a proposed regulatory program under
the authority of sections 110(a)(2)(G), 301, and 303 of the Act. The
March 7, 1995 proposal (60 FR 12492) described this program in greater
detail. Although the intervention level program proposed herein differs
from the section 303 program described in these actions, the basic
objective and the legal authority to establish it remain the same.
Consequently, the EPA continues to rely on the legal authority
discussion regarding sections 301 and 303 contained in the November 15,
1994 proposal and hereby incorporates that discussion by reference (59
FR 58970-71)
ion level program proposed herein differs
from the section 303 program described in these actions, the basic
objective and the legal authority to establish it remain the same.
Consequently, the EPA continues to rely on the legal authority
discussion regarding sections 301 and 303 contained in the November 15,
1994 proposal and hereby incorporates that discussion by reference (59
FR 58970-71).
In addition, the EPA believes that in some cases the potential
health effects that may result from a 5-minute peak SO2
concentration above the concern level of 0.60 ppm could be an indicator
of substantial endangerment to public health and welfare, depending on
the frequency and magnitude of the ambient peak concentrations and the
likelihood that asthmatic individuals will experience exposures of
concern. For example, concentrations above the concern level may
present an unacceptable risk of harm to asthmatic individuals who have
not premedicated with beta-agonist bronchodilators and are exposed at
elevated ventilation. Action under the authority of section 114 to
investigate the cause and potential effect of ambient concentrations
above the concern level, followed by corrective action under the
authority of section 303, might therefore be warranted in some cases.
Furthermore, EPA believes that exposure of a sensitive population to a
5-minute ambient concentration of 2.0 ppm or above would pose an
imminent and substantial endangerment to public health and welfare and,
therefore, would justify corrective action under the authority of
section 303.
Unlike the section 303 program EPA proposed on March 7, 1995, the
intervention level program proposed today would not require States and
tribes to submit revised contingency plans to EPA requiring specific
actions for the State, tribe, and source to undertake once an
established ambient SO2 concentration is violated
erefore, would justify corrective action under the authority of
section 303.
Unlike the section 303 program EPA proposed on March 7, 1995, the
intervention level program proposed today would not require States and
tribes to submit revised contingency plans to EPA requiring specific
actions for the State, tribe, and source to undertake once an
established ambient SO2 concentration is violated. The EPA
believes that the approved SIP's currently in force provide the States
with adequate general authorities to implement the intervention level
program without submittal of revised contingency plans for approval by
EPA. Section 110(a)(2)(G) of the Act requires that the SIP contingency
plans contain adequate authority to implement section 303 programs.
Furthermore, the SIP's contain general enforcement authority that
allows States to request information and conduct inspections--in short,
to gather the necessary data to determine the appropriate course of
action in the event that 5-minute SO2 peaks pose a threat to human
health. Finally, many SIP's contain general prohibitions against air
pollution which provide the States broad discretion to address source-
specific problems. The EPA also believes that once the tribal rule
proposed on August 25, 1994 (59 FR 43956) becomes final, tribal
implementation plans (TIP's) will provide tribes with similar
authority.
The EPA believes the general authority possessed by States and
tribes to implement the intervention level program under section 303 is
an advantage. By eliminating the need for States and tribes to revise
their contingency plans, as well as the need for an extensive review
and approval process, the intervention level program should minimize
the potential administrative burden on the States and tribes. If a
particular State SIP or tribal TIP does not contain adequate authority
to implement the intervention level program, EPA expects the State/
tribe to revise its SIP/TIP accordingly to provide the necessary
authority
, as well as the need for an extensive review
and approval process, the intervention level program should minimize
the potential administrative burden on the States and tribes. If a
particular State SIP or tribal TIP does not contain adequate authority
to implement the intervention level program, EPA expects the State/
tribe to revise its SIP/TIP accordingly to provide the necessary
authority. In the event that the State/tribe does not take prompt
action to revise its SIP/TIP, EPA would issue a SIP/TIP call for the
State/tribe. The EPA interprets sections 110(a)(2)(G) and 303 of the
Act, along with section 301 (which grants general authority to
prescribe regulations necessary to carry out the functions of the
Administrator), as providing adequate legal authority to establish this
program and to promulgate the necessary regulations to implement it.
IV. Program Implementation
A. Requirements Associated with Implementation of the Intervention
Level Program
As stated earlier, EPA's intent in proposing the intervention level
program is that the States and tribes would be given the flexibility to
address particular sources of 5-minute SO2 peak concentrations in
the most efficient and appropriate manner, based on an area-specific
analysis of the particular characteristics of peak ambient
concentration episodes in their jurisdictions. The following discussion
is intended as a guide for implementing the intervention level program
and is not meant to be prescriptive.
The EPA believes that when the concern level of 0.60 ppm has been
exceeded in a given area, the State or tribe should consider whether or
not the situation presents a significant public health risk. If the
number of exceedances per year are few in number, or linked to rare
incidents, the State or tribe may determine that no further action is
warranted unless the frequency or severity of the exceedances
increases
when the concern level of 0.60 ppm has been
exceeded in a given area, the State or tribe should consider whether or
not the situation presents a significant public health risk. If the
number of exceedances per year are few in number, or linked to rare
incidents, the State or tribe may determine that no further action is
warranted unless the frequency or severity of the exceedances
increases. If the concern level is exceeded on a more regular basis, or
to a more severe degree, the State or tribe should conduct a more
detailed analysis. The analysis could include elements such as
identification of the sources that contribute most to the peak ambient
concentrations, the number of observed and projected exceedances, the
magnitude of the exceedances, the nature and location of the sources,
the proximity of the sources to sensitive populations, and other
pertinent factors needed to characterize the risk to public health. The
State or tribe may choose to follow up the analysis with a compliance
inspection of the sources that contribute to the peak ambient
concentrations. If the magnitude of the peak concentrations is
significantly higher than the concern level of 0.60 ppm (but still less
than the endangerment level of 2.0 ppm), the State or tribe may choose
to conduct a compliance inspection after only one exceedance. If any of
the sources under consideration are out of compliance with their
existing emission limits (based on the NAAQS or other air pollution
requirements), then the State or tribe would take the necessary steps
to bring the sources into compliance. If, however, the State or tribe
determines a substantial threat to public health exists, but (1) finds
it unlikely that bringing sources into compliance with their existing
emission limits would prevent further exceedances of the concern level,
or (2) determines the source to be in compliance with applicable
emission limits, then further action in addition to assuring compliance
may be needed
f, however, the State or tribe
determines a substantial threat to public health exists, but (1) finds
it unlikely that bringing sources into compliance with their existing
emission limits would prevent further exceedances of the concern level,
or (2) determines the source to be in compliance with applicable
emission limits, then further action in addition to assuring compliance
may be needed. In such circumstances, the next step would be for the
State, tribe and source to examine the sources of the peak
concentrations. Once that is determined, an appropriate approach to
address the high peak concentrations would need to be developed.
Under the intervention level program, EPA would not specify a time
limit in which States, tribes and sources must take corrective action
(whether it be control devices, process or operational modifications,
or other selected protective approach). However, EPA expects that
development and implementation of any course of corrective action for a
given situation would occur expeditiously and efficiently, based on the
risk to public
health; the specific processes or operations at the source that cause
the peak episodes; the available options for addressing the public
health risk; the reasonable lead time necessary to plan, design,
procure and install control devices and process modifications, or to
implement alternative approaches to control; and other pertinent
considerations. Implementation need not wait until the process of
incorporating the selected course of action into the SIP/TIP, permit,
or other enforceable agreement is complete. Once the approach for
addressing the public health risk has been determined, the State/tribe
should issue a section 303 order to the source to expedite
implementation of the selected action
rol; and other pertinent
considerations. Implementation need not wait until the process of
incorporating the selected course of action into the SIP/TIP, permit,
or other enforceable agreement is complete. Once the approach for
addressing the public health risk has been determined, the State/tribe
should issue a section 303 order to the source to expedite
implementation of the selected action.
In determining the course of corrective action, States, tribes, and
sources should keep in mind that the goal of the intervention level
program is to prevent imminent and substantial endangerment to public
health caused by short-term peak ambient concentrations. Control
measures to prevent recurrences of 5-minute SO2 peaks may include
better maintenance of control equipment, better capture of fugitive
emissions, raising the stack height (refer to section A under
Relationship between the Intervention Level Program and Existing
Programs), restriction of operations during times of peak exposure
(e.g., conducting activities during hours when fewer people are
outside), or other innovative courses of action. In some cases (e.g.,
areas where the risk is minimal due to low population density or where
infrequent 5-minute peaks occur), after consultation with sources and
the affected communities, the State or tribe may determine that control
measures may not be the most appropriate means for reducing the risk to
the public. In such cases, States or tribes, in consultation with
sources and the impacted communities, may elect to address the health
risk through alternative approaches. Examples of alternative approaches
that States, sources, and communities might select are: public
education campaigns for asthma prevention, public warning/notice of
potential health problems due to peak episodes (e.g., a local alert
system, posting of areas where short-term peaks occur), or providing
support for State, tribal, or local public health programs
k through alternative approaches. Examples of alternative approaches
that States, sources, and communities might select are: public
education campaigns for asthma prevention, public warning/notice of
potential health problems due to peak episodes (e.g., a local alert
system, posting of areas where short-term peaks occur), or providing
support for State, tribal, or local public health programs. Should an
alternative approach be chosen, the State/tribe should ensure that the
alternative measures required of the source are federally enforceable.
As the concentration approaches the endangerment level of 2.0 ppm
averaged over a 5-minute period, the health effects, as discussed
earlier, will become more pronounced and severe. The EPA expects States
and tribes will be more concerned about the potential impacts and be
more assertive in pursuing corrective remedies with the sources as the
5-minute peak concentrations approach the endangerment level. At
concentrations at or above the endangerment level, EPA believes that
imminent and substantial endangerment to the public health and welfare
could occur, and if such is the case, urgent corrective actions would
be warranted. However, even an isolated exceedance of the endangerment
level might not require corrective action if the State or tribe find
that the circumstances related to the exceedance are not likely to
reoccur, or that the risk of exposure to sensitive populations is
minimal. Again, EPA encourages States and tribes to determine the
appropriate course of action for each situation based on the potential
for public exposure and the risk to public health. While the State/
tribe would issue section 303 orders requiring urgent corrective
actions, any long-term corrective actions would have the same
enforceability, recordkeeping, and compliance requirements as specified
for the concern level actions
and tribes to determine the
appropriate course of action for each situation based on the potential
for public exposure and the risk to public health. While the State/
tribe would issue section 303 orders requiring urgent corrective
actions, any long-term corrective actions would have the same
enforceability, recordkeeping, and compliance requirements as specified
for the concern level actions.
The EPA believes proper and judicious implementation of the
intervention level program by States and tribes would provide adequate
protection against the recurrence of high, 5-minute SO2 peaks once
such emissions are identified as a problem for particular sources. In
EPA's view, States and tribes, being in the best position to assess the
impact of 5-minute concentrations in their jurisdiction, would have
primary responsibility to execute this section 303 program. However,
EPA would retain the authority to take whatever actions the Agency
considers appropriate under section 303 to address these situations.
For example, if a State or tribe does not take action after the
endangerment level has been exceeded, EPA would consult with the State
or tribe to discuss the basis for their decision not to act. If EPA
then determines that corrective action is warranted to protect public
health, EPA itself would take action. Similarly, EPA would consult with
the State or tribe and take action in cases where it is evident that
frequent exceedances of the concern level constitute an imminent and
substantial endangerment to public health, and the State or tribe has
failed to take protective action.
B. Compliance and Enforcement Issues
ctive action is warranted to protect public
health, EPA itself would take action. Similarly, EPA would consult with
the State or tribe and take action in cases where it is evident that
frequent exceedances of the concern level constitute an imminent and
substantial endangerment to public health, and the State or tribe has
failed to take protective action.
B. Compliance and Enforcement Issues
If the State/tribe decides that action is required under the
intervention level program to abate the threat to public health, an
effective means for ensuring that the source (or sources) has
implemented the required course of action is needed. In many cases,
compliance would consist of the State or tribe ensuring that the source
has implemented the required remedies (e.g., equipment/process
modifications, improving maintenance to address emissions contributing
to short-term peaks, or a system to alert the public that conditions
conducive to high 5-minute peak concentrations are present). However,
if there are instances in which emissions can be feasibly measured on a
5-minute basis, or if fuel sampling can be shown to be a feasible
compliance indicator, the State or tribe may elect to set an emission
limit and use emission measurement or fuel sampling as the method for
determining compliance with any control requirements. In such cases,
ambient air monitoring over a reasonable period after the
implementation of the selected approach would be necessary to verify
the effectiveness of the selected corrective actions.
Enforcement of the intervention level program requirements would be
based on the requirements of the applicable operating permit,
enforceable consent order or agreements, or SIP. Because States and
tribes have differing mechanisms for implementing their programs, EPA
believes States and tribes are in the best position to determine the
most appropriate implementation mechanism for their situations
rcement of the intervention level program requirements would be
based on the requirements of the applicable operating permit,
enforceable consent order or agreements, or SIP. Because States and
tribes have differing mechanisms for implementing their programs, EPA
believes States and tribes are in the best position to determine the
most appropriate implementation mechanism for their situations.
Nonetheless, EPA believes that any corrective action required of a
source by the State/tribe should be effective and practically
enforceable--on both the State/tribal and Federal levels. Furthermore,
the State/tribe should provide opportunity for public notice and
comment on these actions. To this end, SIP revisions, operating
permits, court orders, or other implementation mechanisms that provide
for Federal enforceability and public participation would be
appropriate methods for establishing corrective actions.
V. Relationship Between the Intervention Level Program and Existing
Programs
A. Impact on SIP's, Attainment Planning and Implementation
While both the intervention level program and the SIP address
health concerns caused by ambient concentrations of SO2 in a given
area, care should be taken to distinguish the two approaches. While the
SIP and the intervention level programs are both meant to provide
protection from the effects of ambient SO2 concentrations,
they address different health concerns. The SIP is intended for
implementation of the primary and secondary SO2 NAAQS, established
under sections 108 and 109 of the Act to protect public health with an
adequate margin of safety and protect the public welfare. The limits
for the NAAQS as established are based on an annual arithmetic mean, a
maximum 24-hour concentration and a maximum 3-hour concentration. The
intervention level program, under the authority of section 303, is
designed to address short-term (5-minute) ambient concentrations that
present imminent and substantial endangerment to public health or
welfare
and protect the public welfare. The limits
for the NAAQS as established are based on an annual arithmetic mean, a
maximum 24-hour concentration and a maximum 3-hour concentration. The
intervention level program, under the authority of section 303, is
designed to address short-term (5-minute) ambient concentrations that
present imminent and substantial endangerment to public health or
welfare. While these programs complement each other, satisfaction of
one program's requirements does not necessarily mean compliance with
the other. For example, an area within a State may be in compliance
with the requirements of the SIP and still be subject to 5-minute peaks
of such magnitude and frequency that action under the intervention
level program is warranted. Similarly, in a nonattainment area where
progress is being made toward meeting the SIP requirements, the State/
tribe may conclude that action under the intervention level program is
unnecessary if, for example (1) the area has no 5-minute peaks that
exceed the concern level, or (2) the area has infrequent peak episodes
that do not render a significant health risk. Furthermore, if any
actions are taken by States, tribes, or industry to address 5-minute
peaks of SO2 in a given area, care should be taken to ensure that
such actions do not conflict with the existing SIP requirement, or the
State or tribal attainment plan.
As an example, after investigating 5-minute SO2 peak emissions
in a given area and discussing various approaches with the source and
the affected community, it may be determined that the most cost
efficient way of addressing the situation would be to increase the
stack height of a particular source
ons do not conflict with the existing SIP requirement, or the
State or tribal attainment plan.
As an example, after investigating 5-minute SO2 peak emissions
in a given area and discussing various approaches with the source and
the affected community, it may be determined that the most cost
efficient way of addressing the situation would be to increase the
stack height of a particular source. While the impact of increasing the
stack height may not be considered in determining whether the emission
limitation requirements of the SIP are satisfied, and though the source
may already be in compliance with all applicable SIP limits, it is
conceivable that the best way to address a given 5-minute concentration
problem under the intervention level program could be through the use
of dispersion techniques and intermittent controls. The EPA is not
suggesting by this example that increasing stack heights is generally
an appropriate means for addressing short-term peaks. States, tribes,
sources, and affected communities are encouraged to consider other
available approaches for minimizing the risk from short-term SO2
exposures.
In conclusion, implementation of the intervention level program
cannot and should not lead to any relaxation of the SIP requirements.
However, there will be cases where the implementation of the
intervention level program will complement the implementation of the
SIP, if reductions in emissions are achieved. In nonattainment areas
where 5-minute SO2 peaks are also prevalent, the State or tribe
may wish to coordinate attainment plan development so that the
corrective action taken by the source is consistent with the objectives
of both the attainment plan and the intervention level program.
B. Malfunctions
gram will complement the implementation of the
SIP, if reductions in emissions are achieved. In nonattainment areas
where 5-minute SO2 peaks are also prevalent, the State or tribe
may wish to coordinate attainment plan development so that the
corrective action taken by the source is consistent with the objectives
of both the attainment plan and the intervention level program.
B. Malfunctions
The EPA has on occasion used its enforcement discretion in
determining how and whether to act on unavoidable violations of source
emission limits during periods of startup, shutdown and malfunction (40
CFR 60.11(d)). This policy recognizes that during certain startup and
shutdown conditions, effective pollutant control may sometimes not be
technically feasible due to process temperatures and pressures that
have not yet stabilized. The policy also recognizes that certain source
malfunctions are not reasonably foreseeable and are unavoidable, which
result in uncontrolled emissions to the atmosphere. However, in some
cases these emissions may be causing 5-minute SO2 peak
concentrations that exceed the concern level of 0.60 ppm. The State or
tribe must decide when and if action is needed to address such cases.
The State or tribe may find that if exceedances associated with
malfunctions, start-ups, or shutdowns occur frequently and pose a risk
to public health, an appropriate remedial response (including controls,
improved maintenance, or other alternative approaches) would be
warranted.
C. Significant Harm Level Program
tate or
tribe must decide when and if action is needed to address such cases.
The State or tribe may find that if exceedances associated with
malfunctions, start-ups, or shutdowns occur frequently and pose a risk
to public health, an appropriate remedial response (including controls,
improved maintenance, or other alternative approaches) would be
warranted.
C. Significant Harm Level Program
The EPA views the SHL program and the intervention level program as
separate programs designed to address different situations that pose a
threat to public health. The SHL program establishes corrective actions
in advance to address emergency episodes that occur over a period of
time (in the case of SO2, the timeframe would be 24 hours or
more). The intervention level program is intended to address peak
concentrations which occur over a relatively short timeframe (5
minutes) and, thereby, calls for the appropriate means to address the
peaks to be determined after the peak episode occurs.
In most cases, no overlap between the two programs is expected to
occur. It is, however, conceivable that an area may be subject to high
SO2 emissions and generate 5-minute and 24-hour ambient
concentrations of such magnitude that a State or tribe would have cause
to take action under the auspices of both the intervention level and
the SHL programs. For example, an area experiencing a 24-hour average
SO2 concentration of 1.0 ppm (the significant harm level) would
also experience 5-minute peak concentrations in excess of 0.60 ppm (the
concern level for the intervention level program).
Under such circumstances, EPA expects corrective action will be
promptly initiated through the SHL program
oth the intervention level and
the SHL programs. For example, an area experiencing a 24-hour average
SO2 concentration of 1.0 ppm (the significant harm level) would
also experience 5-minute peak concentrations in excess of 0.60 ppm (the
concern level for the intervention level program).
Under such circumstances, EPA expects corrective action will be
promptly initiated through the SHL program. Once the corrective action
required under that program has been established, steps would be taken
to determine whether (1) that action effectively prevents 5-minute peak
concentration episodes in excess of the intervention levels, or (2) if
the 5-minute episodes occur independently of events in which the 24-
hour episode levels are exceeded. In the latter case, States and tribes
would be expected to take further action under the intervention level
program as necessary.
D. Acid Rain Program
Under the acid rain program, sources (primarily coal-fired electric
utilities) are given flexibility in how they choose to meet their
emissions reductions, including the buying or selling of SO2
emissions allowances. Regardless of the number of SO2 allowances a
source holds, it may not emit at levels that would violate Federal,
State, or tribal emission requirements established under title I of the
Act to protect public health, including any emission requirements that
would be established to carry out the intent of the intervention level
program.
VI. Community Involvement in the Intervention Level Program
As stated earlier, the intervention level program as designed would
give States, tribes, local governments, and communities the authority,
ability and flexibility to address localized health concerns caused by
5-minute SO2 episodes more effectively. While State or tribal
regulatory agencies and industrial sources would be expected to be
primarily responsible for implementing the intervention level program,
members of the local community, whose health may be
give States, tribes, local governments, and communities the authority,
ability and flexibility to address localized health concerns caused by
5-minute SO2 episodes more effectively. While State or tribal
regulatory agencies and industrial sources would be expected to be
primarily responsible for implementing the intervention level program,
members of the local community, whose health may be
significantly impacted by peak ambient SO2 concentrations, have a
primary interest in the implementation of this program. The EPA
encourages the States, tribes, industry, and local citizens to work
together through the intervention level program to identify areas
subject to 5-minute peaks, to assess the need for corrective action,
and to develop corrective solutions.
When identifying areas that are subject to high ambient peaks,
States and tribes may not wish to limit their analysis to ambient air
monitoring and risk analysis. The States and tribes may want to
consider the number and nature of citizen complaints received as an
indicator of a potential public health problem and apply appropriate
resources to receiving, reviewing, and addressing the concerns of
citizens and community groups. The EPA recommends that citizens who
express concern about the health and welfare effects due to high
ambient concentration peaks be given the opportunity to present and
clarify their concerns to the State or tribe. Citizens, in turn, should
be informed of the types and levels of information that would be most
helpful in determining links between peaks and health effects and be
given every opportunity to gather and provide that information. The EPA
can serve as an information resource for States, tribes, and citizens
providing the information it has available regarding health effects,
risk analysis, ambient air concentrations, monitoring, and other
issues, if requested
formation that would be most
helpful in determining links between peaks and health effects and be
given every opportunity to gather and provide that information. The EPA
can serve as an information resource for States, tribes, and citizens
providing the information it has available regarding health effects,
risk analysis, ambient air concentrations, monitoring, and other
issues, if requested.
After the State or tribe completes its assessment of the health
risks in an area caused by 5-minute SO2 concentrations, it may
determine one of three things in an area: (1) measures to protect the
public health are needed, (2) measures to protect the public health are
not needed, or (3) more information is needed to reasonably determine
if protective measures are needed. The EPA encourages States and tribes
to keep local citizens and community groups informed during the
decision-making process, to explain the factors and information used to
supporting the decision, and to provide citizens ample opportunity to
comment if they disagree with the decision.
If the State or tribe decides that measures to protect the public
health are necessary, EPA recommends that the protective measures be
developed through a collaborative process involving the State, tribe,
industry, and the local community. As part of the collaborative
process, the parties involved should determine: (1) an agreed outcome
or goal to be achieved by the protective measures, (2) appropriate
actions to be taken by the emission sources to reduce the risk due to
5-minute ambient SO2 concentrations, (3) a reasonable timetable
for completion of the agreed-upon action (or actions), (4) a process to
ensure that the action (or actions) agreed upon has been taken, and (5)
a reasonable yardstick for assuring that the desired objectives have
been achieved.
VII. Source Prioritization and Monitor Allocation
en by the emission sources to reduce the risk due to
5-minute ambient SO2 concentrations, (3) a reasonable timetable
for completion of the agreed-upon action (or actions), (4) a process to
ensure that the action (or actions) agreed upon has been taken, and (5)
a reasonable yardstick for assuring that the desired objectives have
been achieved.
VII. Source Prioritization and Monitor Allocation
Like the three implementation options originally proposed, a key
element of this new proposed implementation strategy is the relocation
of existing SO2 monitors to areas near point sources where peak
SO2 concentrations may exist. Historically, EPA has relied on
modeling to predict air pollutant concentrations. However, the use of
models is not currently an effective means for predicting 5-minute
SO2 excursions. The reasons for this, discussed in detail in the
March 7, 1995 proposal (60 FR 12492), are summarized as follows: (1)
model validation studies have not been conducted to determine if
existing models can estimate with sufficient accuracy to be used in a
regulatory context; (2) it is difficult to obtain accurate source
emission data for 5-minute periods, since such data often depend on
trying to measure emissions that may occur infrequently and at
unpredictable times, concentrations, and flow rates; and (3) a method
of determining the expected frequency of emission releases due to
malfunctions would have to be employed in order to model these
releases.
For these reasons, EPA presented a ``targeted implementation
strategy'' in the March 7, 1995 proposal that relied principally on
ambient air monitoring instead of modeling to find areas exposed to
high, 5-minute concentrations of SO2. Because the layout of the
existing SLAMS network was intended for characterizing urban ambient
air quality associated with 3-hour, 24-hour, and annual SO2
concentrations, the network is not currently designed to measure 5-
minute peak SO2 concentrations from point sources
d principally on
ambient air monitoring instead of modeling to find areas exposed to
high, 5-minute concentrations of SO2. Because the layout of the
existing SLAMS network was intended for characterizing urban ambient
air quality associated with 3-hour, 24-hour, and annual SO2
concentrations, the network is not currently designed to measure 5-
minute peak SO2 concentrations from point sources. To allow for
the relocation of monitors for measuring 5-minute peak concentrations,
EPA proposed revisions to the ambient air quality surveillance
requirements (40 CFR part 58) and proposed certain technical changes to
the requirements for ambient air monitoring reference and equivalent
methods (40 CFR part 53) in the November 15, 1994 (59 FR 58958) and the
March 7, 1995 (60 FR 12492) proposals. The March 7, 1995 proposal also
presented a strategy States and tribes could use to prioritize
potential sources of high, 5-minute SO2 peaks for monitoring. The
strategy presented three groups of sources ranked by their capacity for
high emission rates and their potential for high, 5-minute peaks.
Available air quality or exposure data and the effects of source
location in complex terrain were also considerations in developing the
groups.
In ranking sources for monitoring 5-minute peaks, EPA did not
expect States and tribes to rely solely on the three categories
described in the original proposal. The EPA also recommended that
States and tribes evaluate each facility on an individual basis,
considering such factors as the type of process, past upsets and
malfunctions, the type of fuel used, the complexity of the surrounding
terrain, knowledge of how well the source is controlled, the compliance
history of the source, proximity to population centers, and the history
of citizen complaints
e EPA also recommended that
States and tribes evaluate each facility on an individual basis,
considering such factors as the type of process, past upsets and
malfunctions, the type of fuel used, the complexity of the surrounding
terrain, knowledge of how well the source is controlled, the compliance
history of the source, proximity to population centers, and the history
of citizen complaints. The States and tribes would also need to
determine how heavily to weigh a Group A source in an area with low
population density versus a Group C source in a more densely-populated
area and consider the impact of different source types clustering
within a given area. These considerations would form the basis for a
State or tribal monitoring plan which would be submitted to EPA during
the annual review of the SLAMS network. While EPA would review the
monitoring plan developed by States or tribes, it was EPA's intent that
States and tribes would retain the main role of decision making since
they would have better knowledge of the individual circumstances
pertaining to the potential sources to be targeted.
Comments received on the targeted monitoring strategy indicate that
some members of the public viewed the proposed strategy as being more
rigid than EPA intended. Many commenters felt that the data and
assumptions used to develop the ranking categories were outdated and/or
conservative. Some felt that their respective industries should not
have been given as high a priority as suggested by the categories. Many
rejected the concept of prioritizing industrial categories, preferring
that the prioritization of sources be based on the additional factors
EPA originally proposed--health and exposure data, the size and
configuration of sources, compliance history, proximity to population
centers, etc.
In response to the comments received, EPA wishes to clarify the
criteria discussed in the March 7, 1995 proposal for use by States and
tribes to prioritize
egories, preferring
that the prioritization of sources be based on the additional factors
EPA originally proposed--health and exposure data, the size and
configuration of sources, compliance history, proximity to population
centers, etc.
In response to the comments received, EPA wishes to clarify the
criteria discussed in the March 7, 1995 proposal for use by States and
tribes to prioritize
the monitoring of sources for high, 5-minute SO2 peaks. The EPA is
not requiring States or tribes to prioritize sources for monitoring in
accordance with the three categories of industrial sources discussed in
that proposal. The EPA is now recommending that States and tribes
evaluate the need to monitor sources based on factors such as the
history of citizen complaints, the compliance history of the sources in
question, the State or tribe's knowledge of the operational
characteristics of a given source (e.g., the likelihood of highly
variable emissions, maintenance history), the population in the
vicinity of a source (or more specifically, the population of
asthmatics and other individuals susceptible to high SO2
concentrations), and environmental justice concerns. The EPA maintains
the proposed revisions to the ambient air quality surveillance
requirements (40 CFR part 58) and the proposed technical changes to the
requirements for ambient air monitoring reference and equivalent
methods (40 CFR part 53), as discussed earlier.
VIII. Reconsideration of Proposed 24-Hour Significant Harm Level and
Episodes Criteria
ons), and environmental justice concerns. The EPA maintains
the proposed revisions to the ambient air quality surveillance
requirements (40 CFR part 58) and the proposed technical changes to the
requirements for ambient air monitoring reference and equivalent
methods (40 CFR part 53), as discussed earlier.
VIII. Reconsideration of Proposed 24-Hour Significant Harm Level and
Episodes Criteria
In the March 7, 1995 action (53 FR 14926), EPA also proposed
revisions to the 24-hour SHL for SO2. The EPA is now reconsidering
this proposed SHL revision.
The EPA based its previous proposal on a reassessment of the data
upon which the original SHL were based and an assessment of more recent
scientific evidence on sulfur oxides and particulate matter. The
scientific evidence suggested that the combination of SO2 and high
levels of particulate matter can be associated with increases in daily
mortality. The final 24-hour PM-10 (particles with an aerodynamic
diameter less than or equal to a nominal 10 micrometers) SHL of 600
g/m3 takes this potential interaction into account. This
raised the question as to whether the remaining SO2 SHL is
sufficient. The possibility that SO2 alone or in combination with
other pollutants or fog droplets may be in part responsible for the
effects associated with 24-hour exposures suggests the need to continue
a 24-hour SHL for SO2, but at a substantially lower concentration.
Accordingly, EPA proposed to revise the 24-hour SO2 SHL from 1.0
(2,620 g/m3) to 0.29 ppm (750 g/m3), as
well as revisions to the 24-hour episode levels.
Upon further consideration, EPA now believes that a revised 24-hour
SHL is not necessary to protect the public health. Based on a review of
existing data, the EPA now believes the additional areas that would
require corrective action as a result of changing the SHL (and the
episode levels) are generally areas that have not attained the SO2
NAAQS
ll as revisions to the 24-hour episode levels.
Upon further consideration, EPA now believes that a revised 24-hour
SHL is not necessary to protect the public health. Based on a review of
existing data, the EPA now believes the additional areas that would
require corrective action as a result of changing the SHL (and the
episode levels) are generally areas that have not attained the SO2
NAAQS. The EPA expects that continued efforts of the States and tribes
toward submittal, approval, and enactment of State or tribal
implementation plans should not only achieve attainment of the NAAQS,
but should also address the impact on human health caused by
significant 24-hour SO2 episodes. For this reason, EPA is amending
its earlier proposal, recommending that no revision to the 24-hour SHL
for SO2 be made at this time. The EPA solicits comment on this
issue.
IX. Comments and the Public Docket
The EPA welcomes comments on all aspects of this proposed
rulemaking. Commenters are especially encouraged to give suggestions
for improving or clarifying any aspects of the proposal. All comments,
with the exception of proprietary information, should be directed to
Docket No. A-94-55 (see ADDRESSES).
Commenters who wish to submit proprietary information for
consideration should clearly separate such information from other
comments by: (1) labeling proprietary information ``Confidential
Business Information,'' and (2) sending proprietary information
directly to the contact person listed (see FOR FURTHER INFORMATION
CONTACT) and not to the public docket. This will help ensure that
proprietary information is not inadvertently placed in the docket. If a
commenter wants EPA to use a submission labeled as confidential
business information as part of the basis for the final rule, then a
nonconfidential version of the document, which summarizes the key data
or information, should be sent to the docket
RMATION
CONTACT) and not to the public docket. This will help ensure that
proprietary information is not inadvertently placed in the docket. If a
commenter wants EPA to use a submission labeled as confidential
business information as part of the basis for the final rule, then a
nonconfidential version of the document, which summarizes the key data
or information, should be sent to the docket. Information covered by a
claim of confidentiality will be disclosed by EPA only to the extent
allowed and by the procedures set forth in 40 CFR part 2. If no claim
of confidentiality accompanies the submission when it is received by
EPA, the submission may be made available to the public without
notifying the commenters.
IX. Administrative Requirements
A. Executive Order 12866
Under Executive Order 12866, the Agency must determine whether a
regulatory action is ``significant'' and, therefore, subject to Office
of Management and Budget (OMB) review and the requirements of the
Executive Order. The order defines a ``significant regulatory action''
as one that may:
(1) Have an annual effect on the economy of $100 million or more or
adversely affect in a material way the economy, a sector of the
economy, productivity, competition, jobs, the environment, public
health or safety, or State, local, or tribal governments or
communities;
(2) create a serious inconsistency or otherwise interfere with an
action taken or planned by another Agency;
(3) materially alter the budgetary impact of entitlements, grants,
user fees, or loan programs or the rights and obligations or recipients
thereof; or
my, productivity, competition, jobs, the environment, public
health or safety, or State, local, or tribal governments or
communities;
(2) create a serious inconsistency or otherwise interfere with an
action taken or planned by another Agency;
(3) materially alter the budgetary impact of entitlements, grants,
user fees, or loan programs or the rights and obligations or recipients
thereof; or
(4) raise novel legal or policy issues arising out of legal
mandates, the President's priorities, or the principles set forth in
the Executive Order.
While EPA does not believe the intervention level program would
potentially have an annual effect on the economy of $100 million or
more, the proposed intervention level program was developed in part due
to comments received on earlier proposed implementation strategies
which were deemed to be significant. Also, to some extent, the
characteristics of the intervention level program--local
responsibility, flexibility, community involvement--represents a novel
regulatory approach. For these reasons, EPA has judged that the
proposed intervention level program is a significant regulatory action
as defined by Executive Order 12866 and has submitted this action to
OMB for review. The EPA has prepared a regulatory impact analysis (RIA)
which is summarized below.
In the event that a State or tribe determines that some means of
corrective action is necessary under the intervention level program,
the actions taken will be specific to the source and the area impacted
by high, 5-minute ambient concentrations. As such, the costs can vary
widely (from a low-cost alternative, such as fuel switching, to the
installation of more costly add-on control equipment). Because of the
tremendous uncertainty surrounding the estimation of national costs,
the RIA evaluates the cost of control through a series of case studies
that present information on a sample of control strategies
minute ambient concentrations. As such, the costs can vary
widely (from a low-cost alternative, such as fuel switching, to the
installation of more costly add-on control equipment). Because of the
tremendous uncertainty surrounding the estimation of national costs,
the RIA evaluates the cost of control through a series of case studies
that present information on a sample of control strategies. The case
studies chosen for analysis in the RIA are based upon available data
and characteristics of the SO2 problem (and areas) that provide a
broad scope of the issues associated with the implementation of the
intervention level program. Of the predicted actions to be taken under
this program, two of them correspond with case studies provided in the
RIA. It should be noted, however, that the control strategies evaluated
for the case
studies were chosen to provide the reader with a wide variety of
approaches to resolve a short-term SO2 problem, and thus, the
strategies may not coincide with strategies that may be developed by
States and tribes to resolve the problem in their local areas. The list
of control strategies analyzed is not exhaustive, as time and resource
constraints preclude analysis of all possible control alternatives
(including new and innovative ways of addressing SO2
concentrations that States and local communities may develop while
evaluating a 5-minute SO2 problem). As discussed earlier, States
or tribes may choose to have sources address health risks from short-
term peaks through alternative approaches such as public health
education campaigns or public warning/notice of peak episodes. Such
approaches may have lower costs than measures that reduce SO2
emissions.
Since the current SLAMS network was not developed to identify areas
that experience 5-minute peak SO2 concentrations, it is difficult
to predict how many areas of concern might be identified by States and
tribes when they relocate monitors for this purpose
cation campaigns or public warning/notice of peak episodes. Such
approaches may have lower costs than measures that reduce SO2
emissions.
Since the current SLAMS network was not developed to identify areas
that experience 5-minute peak SO2 concentrations, it is difficult
to predict how many areas of concern might be identified by States and
tribes when they relocate monitors for this purpose. A survey of the
States yielded 63 source-based monitors that monitored 5-minute
concentrations during 1993 and 1994. Of these 63 monitors, 27 (43
percent) registered at least one exceedance of the concern level (0.6
ppm), and 1 (2 percent) registered exceedance of the endangerment level
(2.0 ppm). Based on a detailed evaluation of data from these monitors,
EPA identified ten areas that the Agency felt would be evaluated for
the level of public health risk associated with short-term SO2
episodes. Of the ten areas, EPA reasonably estimates that action under
the intervention level program could be warranted for approximately
five areas. The EPA is using several types of information as a basis
for projecting the likelihood of action under the intervention level
program, including: (1) historical knowledge about the situation based
on interactions between the EPA Regions, States and local sources; (2)
comments from sources, States, and local agencies on the original
proposals which not only discuss local situations, but also the
regulatory agency's likely response (because EPA is not only making a
provisional judgment about the potential public health risk from these
situations, but is also assessing how the regulatory agencies would
respond); (3) air quality and census data; and (4) information about
the industrial processes at facilities in the locations of concern.
The EPA recognizes that relocation of monitors around sources and
in areas of potential concern could identify more areas where
assessment of public health risk and possible intervention would be
warranted
is also assessing how the regulatory agencies would
respond); (3) air quality and census data; and (4) information about
the industrial processes at facilities in the locations of concern.
The EPA recognizes that relocation of monitors around sources and
in areas of potential concern could identify more areas where
assessment of public health risk and possible intervention would be
warranted. Since there is significant uncertainty about the extent to
which States and tribes will relocate monitors, the total cost of the
final program could be higher than the cost EPA has so far identified.
The EPA invites public comment on its approach to estimating the costs
of this proposal.
The case studies indicate the range of annualized cost for
solutions to different 5-minute SO2 problems to be from
approximately $300,000 to $2.2 million. In addition, some case studies
have no cost associated with the program since action is not taken.
Yet, other studies indicate the potential for either a cost savings of
$257,544 or a total annualized cost of $30 million. The range of costs
reflects the significant amount of flexibility that regulatory
authorities, communities, and sources have under the intervention level
program to resolve short-term SO2 problems at a substantially
lower cost than other potential regulatory vehicles. For example, the
previously-proposed regulatory option of establishing a new short-term
SO2 NAAQS (0.60 ppm, 5-minute average) was estimated to cost $1.75
billion. Several sources expected to incur costs under the NAAQS option
would conceivably have no regulatory action taken upon them under the
intervention level program and thus would not incur compliance costs.
Even if the five actions predicted so far to occur under the
intervention level program have the highest end of costs estimated in
the RIA case studies ($2.2 million), the total cost of these five
actions would be $11 million--$1.739 billion less than the NAAQS option
proposed earlier
atory action taken upon them under the
intervention level program and thus would not incur compliance costs.
Even if the five actions predicted so far to occur under the
intervention level program have the highest end of costs estimated in
the RIA case studies ($2.2 million), the total cost of these five
actions would be $11 million--$1.739 billion less than the NAAQS option
proposed earlier.
Given that implementation of the intervention level program will
only occur in areas where a State or tribe determines there is
substantial risk to human health, it is unlikely that a vast number of
sources in any one industry will be impacted. It is likely that only
one or two sources of an industry will incur additional control costs
to resolve a 5-minute SO2 problem. If the sources affected by the
program are not the marginal producers of an industry, the market
supply curve is not likely to shift and the source would not benefit
from increased prices. Rather, the source would absorb the compliance
costs and incorporate them into the cost of production to determine
their optimal level of operation.
The quantified benefits of the case studies ranged in value from
$2,700 to $44,100. As such, the costs exceed benefits by a significant
amount. The small magnitude of benefits results from mainly two
factors. First, the short-term peaks in SO2 under consideration
impact a fairly small geographic area within the local vicinity of the
model plants. The small geographic area leads to a relatively small
number of people being exposed to these short-term peaks. Second, the
benefit estimates are limited to the health benefits accruing to
asthmatics. The welfare benefits associated with any ecosystem--
visibility, odor, materials damage, or particulate matter improvements
that may result from control of short-term peaks in SO2--have not
been considered
eographic area leads to a relatively small
number of people being exposed to these short-term peaks. Second, the
benefit estimates are limited to the health benefits accruing to
asthmatics. The welfare benefits associated with any ecosystem--
visibility, odor, materials damage, or particulate matter improvements
that may result from control of short-term peaks in SO2--have not
been considered. Although the costs determined for the case studies
exceed the quantifiable benefits, the intervention level program
achieves a reasonable solution to short-term SO2 problems at
substantially lower cost than other potential regulatory vehicles, such
as the previously-proposed, new short-term SO2 NAAQS. Several of
the sources assumed to incur costs under the short-term NAAQS option
would conceivably not require regulatory action taken upon them under
the proposed intervention level program and would thus incur no
compliance costs. In addition, a regulatory authority may consider
environmental justice as a criteria to warrant action under the
intervention level program. Paragraph E of this section of the preamble
discusses the environmental justice analysis prepared for the RIA.
B. Monitoring and Administration Costs
There are 679 sites in the current SLAMS network established to
monitor for violations of the SO2 NAAQS. It was estimated in the
previous proposal that approximately two-thirds of the monitors could
be relocated in order to monitor for short-term SO2 concentrations
without compromising the current network of monitors for the NAAQS.
When final changes to the requirements for ambient air monitoring
reference and equivalent methods (40 CFR part 53) and revisions to the
ambient air quality surveillance requirements (40 CFR part 58) are
promulgated, the States, tribes, and local authorities will be given
guidance to place anywhere from 1 to 4 monitors around sources where
short-term SO2 concentrations are of concern
NAAQS.
When final changes to the requirements for ambient air monitoring
reference and equivalent methods (40 CFR part 53) and revisions to the
ambient air quality surveillance requirements (40 CFR part 58) are
promulgated, the States, tribes, and local authorities will be given
guidance to place anywhere from 1 to 4 monitors around sources where
short-term SO2 concentrations are of concern. While the total
number of monitors to be relocated cannot be determined presently, it
is likely that significantly fewer than two-thirds of the current
network will be relocated under the intervention level program.
The cost to relocate a monitor is specific to the monitor and site.
However, if a stand-alone monitor can be relocated without having to
replace operating and maintenance equipment (i.e., the shelter,
calibration equipment, data logger, etc.), EPA estimates it would cost
$18,630 to relocate the monitor. If a monitor that is relocated
requires the installation of new equipment, the total cost of
relocation would be $45,050. In addition, there is a cost to operate
the monitor estimated at $22,000 per year. If the monitor is currently
operating independently, relocating the monitor would merely transfer
this expense to the new site. Therefore, there would be no incremental
cost to operate the relocated monitor. However, the EPA is aware that
some SO2 monitors are colocated with other monitors (e.g., for
ozone, nitrogen oxides, and particulate matter). When relocating the
SO2 monitor in this case, the existing site would maintain the
current operating expense for the remaining monitors, and the new site
for the relocated SO2 monitor would incur an incremental operating
cost of $22,000. Thus the total cost to relocate a monitor could range
from $18,630 for a stand-alone monitor that already has the necessary
equipment to relocate to a new site and will not incur any incremental
operating costs to $67,050 for a monitor requiring both new equipment
and operating expenses
tors, and the new site
for the relocated SO2 monitor would incur an incremental operating
cost of $22,000. Thus the total cost to relocate a monitor could range
from $18,630 for a stand-alone monitor that already has the necessary
equipment to relocate to a new site and will not incur any incremental
operating costs to $67,050 for a monitor requiring both new equipment
and operating expenses.
The EPA recognizes that as monitors are relocated, areas of concern
in addition to those estimated may be identified. To the extent more
information becomes available, EPA will estimate the anticipated impact
of relocating monitors on total program costs in the final rule.
The EPA recognizes that there are costs associated with the
administration of the intervention level program. These costs include:
determining the need to relocate monitors; evaluating citizen
complaints; assessing public health risk; and developing, implementing,
and monitoring actions required of the source to reduce risk. The EPA
believes that the additional costs resulting from the intervention
level program would be minimal for two reasons. First, many States and
tribes currently have sufficient administrative infrastructure in place
to conduct such activities. Second, the flexibility of the program
allows States and tribes to use their resources in the most efficient
manner in implementing the program. The EPA invites public comment on
the costs associated with administering the intervention level program.
C. Regulatory Flexibility Analysis
ates and
tribes currently have sufficient administrative infrastructure in place
to conduct such activities. Second, the flexibility of the program
allows States and tribes to use their resources in the most efficient
manner in implementing the program. The EPA invites public comment on
the costs associated with administering the intervention level program.
C. Regulatory Flexibility Analysis
The Regulatory Flexibility Act (RFA) requires that all Federal
agencies consider the impacts of final regulations on small entities,
which are defined to be small businesses, small organizations, and
small governmental jurisdictions (5 U.S.C. 601 et seq.). Under 5 U.S.C.
605(b), this requirement may be waived if the Agency certifies that the
rule will not have a significant economic effect on a substantial
number of small entities. Small entities include small businesses,
small not-for-profit enterprises, and governmental entities with
jurisdiction over populations of less than 50,000.
A decision to implement the intervention level program under the
authority of section 303 would impose no new major requirements.
Furthermore, the control measures necessary to implement the
intervention level program are developed by the States and tribes. In
selecting such measures, the States and tribes have considerable
discretion to address the risk presented by 5-minute ambient SO2
concentrations. Therefore, the impact on small entities from the
intervention level program would be determined by how the States and
tribes choose to implement the program. For these reasons, any
assessment performed by EPA on the costs of implementation at this time
would necessarily be speculative. On the basis of the above
considerations and findings, and as required by section 605 of the RFA,
5 U.S.C. 601 et seq., the Administrator certifies that this regulation
does not have a significant impact on a substantial number of small
entities.
D. Impact on Reporting Requirements
any
assessment performed by EPA on the costs of implementation at this time
would necessarily be speculative. On the basis of the above
considerations and findings, and as required by section 605 of the RFA,
5 U.S.C. 601 et seq., the Administrator certifies that this regulation
does not have a significant impact on a substantial number of small
entities.
D. Impact on Reporting Requirements
While there are reporting requirements associated with related
sections of the Act, particularly sections 107, 110, 160, and 317 (42
U.S.C. 7407, 7410, 7460, and 7617), there are no specific Federal
reporting requirements associated with the proposed intervention level
program. Because the program gives States and tribes discretion to take
action as warranted by the risk to the public health, it is difficult
to project what recordkeeping and reporting requirements States and
tribes may feel are needed to ensure compliance and enforceability in
specific cases. Furthermore, any necessary reporting and recordkeeping
would be restricted to sources the State/tribe determines as
contributing to high 5-minute concentrations in a localized area. No
recordkeeping or reporting would be required from sources not
contributing to 5-minute peaks or from sources in areas not subject to
high 5-minute peaks.
Consequently, EPA is not asking for approval under the Paperwork
Reduction Act for any such requirements at this time. The EPA welcomes
comments on the nature and burden of recordkeeping and reporting
requirements that may be associated with the intervention level
program. As the information requirements of the program become clearer,
EPA will reevaluate the need for information collection approval under
the Paperwork Reduction Act.
E. Unfunded Mandates Reform Act
Act for any such requirements at this time. The EPA welcomes
comments on the nature and burden of recordkeeping and reporting
requirements that may be associated with the intervention level
program. As the information requirements of the program become clearer,
EPA will reevaluate the need for information collection approval under
the Paperwork Reduction Act.
E. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), P.L.
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 sections 202, 203, and 205,
respectively, of the UMRA, EPA generally must prepare a written
statement, including a cost-benefit analysis, for proposed and final
rules with ``Federal mandates'' that may result in expenditures to
State, local and tribal governments, in the aggregate or to the private
sector, of $100 million or more in any 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 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 a small government agency
plan under section 203 of the UMRA
east costly, most cost-
effective or least burdensome alternative if the Administrator
publishes with the final rule an explanation why that alternative was
not adopted. Before EPA establishes any regulatory requirements that
may significantly or uniquely affect small governments, including
tribal governments, it must have developed a small government agency
plan under section 203 of the UMRA. The plan must provide for notifying
potentially-affected, small governments, enabling officials of affected
small governments to have meaningful and timely input in the
development of EPA regulatory proposals with significant Federal
intergovernmental mandates, and informing, educating, and advising
small governments on compliance with the regulatory requirements.
The EPA has determined that this proposal does not contain a
Federal mandate that may result in expenditures
of $100 million or more for State, local, or tribal governments, in the
aggregate or the private sector in any 1 year. The EPA anticipates that
the number of cases in which abatement of short-term SO2
concentrations will be necessary will be few in number and that the
States and tribes will work with the sources and the local community to
arrive at the most appropriate and efficient control approach to reduce
the risk to the public. For these reasons, the expenditures under the
intervention level program are not expected to exceed the $100 million
threshold. Thus, today's proposal is not subject to the requirements of
sections 202 and 205 of the UMRA.
F. Environmental Justice
l work with the sources and the local community to
arrive at the most appropriate and efficient control approach to reduce
the risk to the public. For these reasons, the expenditures under the
intervention level program are not expected to exceed the $100 million
threshold. Thus, today's proposal is not subject to the requirements of
sections 202 and 205 of the UMRA.
F. Environmental Justice
Executive Order 12898 requires that each Federal agency shall make
achieving environmental justice part of its mission by identifying and
addressing, as appropriate, disproportionately high and adverse human
health or environmental effects of its programs, policies, and
activities on minority and low-income populations. The requirements of
Executive Order 12898 have been addressed in the draft regulatory
impact analysis.
A number of factors indicate that asthma may pose more of a health
problem among non-white individuals, children, and urban populations.
With these factors in mind, a general screening analysis is conducted
to examine the sociodemographic characteristics of the case study areas
potentially impacted by short-term SO2 peaks.
Overall, the population distributions in the case study areas do
not indicate that a disproportionate number of non-white individuals
would be impacted by short-term SO2 ambient concentrations greater
than 0.60 ppm. The analysis also indicates that there are twice as many
children residing in the case study areas as compared to the national
average, and potentially 595 of these children could have asthma and
thus experience health impacts during peak SO2 concentrations. In
addition to the large number of children potentially exposed to peak
SO2 concentrations, 27 percent of the households in the case study
areas are below the poverty level, which is twice the national average.
It should be noted, however, that it is not known how many of the
households below the poverty level contain asthmatic individuals
rience health impacts during peak SO2 concentrations. In
addition to the large number of children potentially exposed to peak
SO2 concentrations, 27 percent of the households in the case study
areas are below the poverty level, which is twice the national average.
It should be noted, however, that it is not known how many of the
households below the poverty level contain asthmatic individuals. Given
the available data, there is an indication that a disproportionate
number of children and households below the poverty level are exposed
to short-term SO2 peaks.
In general, children do not have sufficient resources to relocate
or take action against sources of SO2 emissions. Similarly,
households below the poverty level are generally unlikely to relocate
or take action against sources of SO2 emissions. Not only do these
households often lack the resources to relocate, but they may be
dependent on the local industrial sources for employment. In such a
case, these households may be reluctant to take action against sources
of SO2 emissions if this action would adversely impact employment
opportunities.
List of Subjects in 40 CFR Part 51
Environmental protection, Administrative practices and procedure,
Air pollution control, Intergovernmental relations, SO2, Reporting
and recordkeeping requirements, State implementation plans.
Dated: December 20, 1996.
Carol M. Browner,
Administrator.
References
nst sources
of SO2 emissions if this action would adversely impact employment
opportunities.
List of Subjects in 40 CFR Part 51
Environmental protection, Administrative practices and procedure,
Air pollution control, Intergovernmental relations, SO2, Reporting
and recordkeeping requirements, State implementation plans.
Dated: December 20, 1996.
Carol M. Browner,
Administrator.
References
EPA (1982a), Air Quality Criteria for Particulate Matter and Sulfur
Oxides, Environmental Criteria and Assessment Office, Research
Triangle Park, NC, EPA-600/8-82-029a-c.
EPA (1982b), Review of the National Ambient Air Quality Standards
for Sulfur Oxides: Assessment of Scientific and Technical
Information--OAQPS Staff Paper, Office of Air Quality Planning and
Standards, Research Triangle Park, NC, EPA-450/5-82-007.
EPA (1986a), Second Addendum to Air Quality Criteria for Particulate
Matter and Sulfur Oxides (1982): Assessment of Newly Available
Health Effects Information, Environmental Criteria and Assessment
Office, Research Triangle Park, NC, EPA-450/5-86-012.
EPA (1986b), Review of the National Ambient Air Quality Standards
for Sulfur Oxides: Updated Assessment of Scientific and Technical
Information, Addendum to the 1982 OAQPS Staff Paper, Office of Air
Quality Planning and Standards, Research Triangle Park, NC EPA-450/
05-86-013.
EPA (1994a), Supplement to the Second Addendum (1986) to Air Quality
Criteria for Particulate Matter and Sulfur Oxides (1982): Assessment
of New Findings on Sulfur Dioxide Acute Exposure Health Effects in
Asthmatic Individuals, Environmental Criteria and Assessment Office,
Research Triangle Park, NC, EPA/600/FP-93/002.
EPA (1994b), Review of the Ambient Air Quality Standards for Sulfur
Oxides: Updated Assessment of Scientific and Technical Information,
Supplement to the 1986 OAQPS Staff Paper Addendum, Office of Air
Quality Planning and Standards, Research Triangle Park, NC, EPA/452/
R-94-01
Horstman, D. H. Roger, L. J.; Kehrl, H. R.; Hazucha, M. J. (1986)
fice,
Research Triangle Park, NC, EPA/600/FP-93/002.
EPA (1994b), Review of the Ambient Air Quality Standards for Sulfur
Oxides: Updated Assessment of Scientific and Technical Information,
Supplement to the 1986 OAQPS Staff Paper Addendum, Office of Air
Quality Planning and Standards, Research Triangle Park, NC, EPA/452/
R-94-01
Horstman, D. H. Roger, L. J.; Kehrl, H. R.; Hazucha, M. J. (1986).
Airway sensitivity of asthmatics to sulfur dioxide. Toxicol. Ind.
Health. 2:289-298.
Roger, L. J.; Kehrl, H. R.; Hazucha, M.; Horstman, D. H. (1985).
Bronchoconstriction in asthmatics exposed to sulfur dioxide during
repeated exercise. J. Appl. Physiol. 59: 784-791.
For the reasons set forth in the preamble, EPA proposes to amend
part 51 of Chapter I of title 40 of the Code of Federal Regulations as
follows:
PART 51--REQUIREMENTS FOR PREPARATION, ADOPTION, AND SUBMITTAL OF
IMPLEMENTATION PLANS
1. The authority citation for part 51 continues to read as follows:
Authority: 42 U.S.C. 7401-7671q.
Subpart H--Prevention of Air Pollution Emergency Episodes
2. Section 51.154 is added to Subpart H to read as follows:
Sec. 51.154 Intervention levels.
(a) Each plan must contain the authority to take whatever action
necessary to prevent further exceedances of the following concern level
attributable to emissions from a source or group of sources where one
exceedance has occurred, and the State, tribe, or local air pollution
control agency determines that the potential for further exceedances of
this level constitutes imminent and substantial endangerment to public
health or welfare, or the environment:
Sulfur dioxide (SO2)--0.60 ppm, 5-minute hourly maximum
value.
n level
attributable to emissions from a source or group of sources where one
exceedance has occurred, and the State, tribe, or local air pollution
control agency determines that the potential for further exceedances of
this level constitutes imminent and substantial endangerment to public
health or welfare, or the environment:
Sulfur dioxide (SO2)--0.60 ppm, 5-minute hourly maximum
value.
(b) Each plan must contain the authority to take whatever action
necessary to prevent further exceedances of the following endangerment
level attributable to emissions from a source or group of sources where
one exceedance has occurred, and the State, tribe, or local air
pollution control agency determines that the potential for further
exceedances of this level constitutes imminent and substantial
endangerment to public health or welfare, or the environment:
Sulfur dioxide (SO2)--2.0 ppm, 5-minute hourly maximum
value.
(c) Nothing in paragraphs (a) or (b) of this section shall preclude
the State, tribe, or local air pollution control agency from addressing
any public health threat arising from exceedances of the concern or
endangerment levels with measures other than the imposition
of control requirements designed to reduce emissions from specific
sources, as long as the measures chosen effectively reduce the threat
to public health.
(d) The State, tribe, or local air pollution control agency shall
ensure that any action to be taken on the part of the source or group
of sources to address any public health threat caused by exceedances of
either the concern or endangerment level shall be enforceable by the
Administrator and by citizens under the Act.
g as the measures chosen effectively reduce the threat
to public health.
(d) The State, tribe, or local air pollution control agency shall
ensure that any action to be taken on the part of the source or group
of sources to address any public health threat caused by exceedances of
either the concern or endangerment level shall be enforceable by the
Administrator and by citizens under the Act.
(e) A 5-minute hourly maximum value for SO2 is the highest of
the 5-minute averages from the 12 possible nonoverlapping periods
during a clock hour. An exceedance occurs if the 5-minute hourly
maximum is greater than the 5-minute concern or endangerment level
after rounding. A value of 0.605 would be rounded to 0.61; a value of
2.05 would be rounded to 2.1. Therefore, the smallest value for an
exceedance of the concern level is 0.61 and the smallest value for an
exceedance of the endangerment level is 2.1. A 5-minute maximum shall
be considered valid if:
(1) The 5-minute averages were available for at least 9 of the 12
5-minute periods during the clock hour; or
(2) The value of any 5-minute average is greater than the concern
level.
[FR Doc. 96-32978 Filed 12-31-96; 8:45 am]
BILLING CODE 6560-50-P
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