99-19433. Air Quality Index Reporting  

  • [Federal Register Volume 64, Number 149 (Wednesday, August 4, 1999)]
    [Rules and Regulations]
    [Pages 42530-42549]
    From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
    [FR Doc No: 99-19433]
    
    
    
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    Part III
    
    
    
    
    
    Environmental Protection Agency
    
    
    
    
    
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    40 CFR Part 58
    
    
    
    Air Quality Index Reporting; Final Rule
    
    Federal Register / Vol. 64, No. 149 / Wednesday, August 4, 1999 / 
    Rules and Regulations
    
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    ENVIRONMENTAL PROTECTION AGENCY
    
    40 CFR Part 58
    
    [FRL-6409-7]
    RIN 2060-AH92
    
    
    Air Quality Index Reporting
    
    AGENCY: Environmental Protection Agency (EPA).
    
    ACTION: Final rule.
    
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    SUMMARY: Today, EPA adopts revisions to the uniform air quality index 
    used by States for daily air quality reporting to the general public in 
    accordance with section 319 of the Clean Air Act (Act). These changes 
    include the addition of the following elements: a new category 
    described as ``unhealthy for sensitive groups;'' two new requirements, 
    first, to report a pollutant-specific sensitive group statement when 
    the index is above 100, and second, to use specific colors if the index 
    is reported in a color format; new breakpoints for the ozone 
    (03) sub-index in terms of 8-hour average 03 
    concentrations; a new sub-index for fine particulate matter 
    (PM2.5); and conforming changes to the sub-indices for 
    coarse particulate matter (PM10), carbon monoxide (CO), and 
    sulfur dioxide (SO2). In addition, EPA is changing the name 
    of the index from the Pollutant Standards Index (PSI) to the Air 
    Quality Index (AQI). This document discusses the development of related 
    informational materials on pollutant-specific health effects and 
    sensitive groups and on precautionary actions that can be taken by 
    individuals to reduce exposures of concern. This document also 
    discusses the interrelationship between the uniform air quality index 
    and other programs that provide air quality information and related 
    health information to the general public, including State and local 
    real-time air quality data mapping and community action programs.
    
    EFFECTIVE DATE: October 4, 1999.
    
    ADDRESSES: A docket containing information relating to EPA's revisions 
    of the air quality index (Docket No. A-98-20) is available for public 
    inspection in the Air and Radiation Docket and Information Center, U.S. 
    Environmental Protection Agency, South Conference Center, Room M-1500, 
    401 M St., SW, Washington, DC 20460, telephone (202) 260-7548. The 
    docket may be inspected between 8 a.m. and 5:30 p.m. on weekdays, and a 
    reasonable fee may be charged for copying. For the availability of 
    related information, see SUPPLEMENTARY INFORMATION.
    
    FOR FURTHER INFORMATION CONTACT: Terence Fitz-Simons, EPA (MD-14), 
    Research Triangle Park, NC 27711, telephone (919) 541-0889, e-mail 
    fitz-simons.terence@epa.gov. For health effects information, contact 
    Susan Lyon Stone, EPA (MD-15), Research Triangle Park, NC 27711, 
    telephone (919) 541-1146, e-mail stone.susan@epa.gov.
    
    SUPPLEMENTARY INFORMATION: In compliance with President Clinton's June 
    1, 1998 Executive Memorandum on Plain Language in government writing, 
    this package is written using plain language. Thus, the use of ``we'' 
    or ``us'' in this package refers to EPA. The use of ``you'' refers to 
    the reader and may include industry, State and local agencies, 
    environmental groups and other interested individuals.
    
    Availability of Related Information
    
        Certain documents are available from the U.S. Department of 
    Commerce, National Technical Information Service, 5285 Port Royal Road, 
    Springfield, VA 22161. Available documents include:
        (1) The Review of the National Ambient Air Quality Standards for 
    Ozone: Assessment of Scientific and Technical Information (``Staff 
    Paper'') (EPA-452/R-96-007, June 1996, NTIS # PB-96-203435, $67.00 
    paper copy and $21.50 microfiche). (Add a $3.00 handling charge per 
    order.)
        (2) Review of the National Ambient Air Quality Standards for 
    Particulate Matter: Policy Assessment of Scientific and Technical 
    Information (``Staff Paper'') (EPA-452/R-96-013, July 1996, NTIS # PB-
    97-115406, $47.00 paper copy and $19.50 microfiche). (Add a $3.00 
    handling charge per order.)
        The guidance documents associated with this rulemaking are 
    available from EPA's Office of Air Quality Planning and Standards in 
    Research Triangle Park, NC. Requests for these publications can be 
    mailed to: Terence Fitz-Simons, EPA (MD-14), Research Triangle Park, NC 
    27711. Your request may also be phoned in to Terence Fitz-Simons at 
    919-541-0889, or sent by e-mail to fitz-simons.terence@epa.gov.
        (1) Guideline for Public Reporting of Daily Air Quality--Air 
    Quality Index (AQI) (EPA-454/R-99-010).
        (2) Guideline for Developing an Ozone Forecasting Program (EPA-454/
    R-99-009).
        The following document is available from EPA's Office of Mobile 
    Sources (OMS) in Ann Arbor, MI. Requests for this publication can be 
    mailed to: Michael Ball, US EPA--National Vehicle and Fuel Emissions 
    Laboratory (NVFEL), 2000 Traverwood Dr., Ann Arbor, MI 48103. Your 
    request may also be phoned in to Michael Ball at 734-214-4897, or sent 
    by e-mail to ball.michael@epa.gov.
        (1) Community Action Programs: Blueprint for Program Design (EPA 
    420-R-98-003).
    
    Table of Contents
    
    I. Background
        A. What Are the Legislative Requirements?
        B. What Is the History of the Air Quality Index?
        C. What Programs Are Related to the AQI?
        1. Ozone and Particulate Matter NAAQS Revisions
        2. Real-Time Data Reporting Initiative (Ozone Mapping Project)
        3. Community Action Programs
    II. Rationale for Final Revisions
        A. What Revisions Did We Propose?
        1. What Were the Proposed General Changes?
        2. What Were the Proposed Changes to the Sub-Indices?
        B. What Were the Significant Comments and Our Responses?
        1. Comments and Responses on General Changes
        2. Comments and Responses on Changes to the Sub-Indices
        C. What Are the Final Revisions?
        1. What Are the General Changes?
        2. What Are the Changes to the Sub-Indices?
        D. What Are the Related Informational Materials?
    III. Regulatory and Environmental Impact Analyses
        A. Executive Order 12866: OMB Review of ``Significant Actions''
        B. Regulatory Flexibility Analysis/Small Business Regulatory 
    Enforcement Fairness Act
        C. Unfunded Mandates Reform Act
        D. Paperwork Reduction Act
        E. Executive Order 13045: Children's Health
        F. Executive Order 12848: Environmental Justice
        G. Executive Order 12875: Enhancing Intergovernmental 
    Partnerships
        H. Executive Order 13084: Consultation and Coordination with 
    Indian Tribal Governments
        I. National Technology Transfer and Advancement Act
        J. Congressional Review Act
    IV. References
    
    I. Background
    
    A. What Are the Legislative Requirements?
    
        Section 319 of the Act governs the establishment of a uniform air 
    quality index for reporting of air quality. This section directs the 
    Administrator to ``promulgate regulations establishing an air quality 
    monitoring system throughout the United States which utilizes uniform 
    air quality monitoring criteria and methodology and measures such air 
    quality according to a uniform air quality index'' and ``provides for 
    daily analysis and reporting of air
    
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    quality based upon such uniform air quality index * * *''.
    
    B. What Is the History of the Air Quality Index?
    
        In 1976, we established a nationally uniform AQI, called the 
    Pollutant Standards Index (PSI), for use by State and local agencies on 
    a voluntary basis (41 FR 37660). This uniform index was established in 
    light of a study conducted by EPA and the President's Council on 
    Environmental Quality (CEQ, 1976). This study found that the 55 urban 
    areas in the U.S. and Canada reporting an index of air quality used 14 
    different indices, in conjunction with different cautionary messages, 
    such that in essence 55 different indices were being used to report air 
    quality. This diversity of indices sent a confusing message about air 
    quality to the public. Based in part on this study, we developed an 
    index to meet the needs of State and local agencies that has the 
    following advantages: it sends a clear and consistent message to the 
    public by providing nationally uniform information on air quality; it 
    is keyed as appropriate to the national ambient air quality standards 
    (NAAQS) and the significant harm level (SHL) 1 which have a 
    scientific basis relating air quality and public health; it is simple 
    and easily understood by the public; it provides a framework for 
    reflecting changes to the NAAQS; and it can be forecasted to provide 
    advance information on air quality.
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        \1\ Significant harm levels are those ambient concentrations of 
    air pollutants that present an imminent and substantial endangerment 
    to public health or welfare, or to the environment, as established 
    in 40 CFR 51.151.
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        The PSI, which is also commonly referred to by some State and local 
    agencies as the AQI, includes sub-indices for O3, PM, CO, 
    SO2, and nitrogen oxide (NO2), which relate 
    ambient pollutant concentrations to index values on a scale from 0 
    through 500. This represents a very broad range of air quality, from 
    pristine air to air pollution levels that present imminent and 
    substantial endangerment to the public. The index has historically been 
    normalized across pollutants by defining an index value of 100 as the 
    numerical level of the short-term (i.e., averaging time of 24-hours or 
    less) primary NAAQS for each pollutant and an index value of 500 as the 
    SHL.2 Such index values serve to divide the index into 
    categories, with each category being identified by a simple informative 
    descriptor. The descriptors are intended to convey to the public 
    information about how air quality within each category relates to 
    public health, with increasing public health concerns being conveyed as 
    the categories range to the upper end of the scale. Additional 
    information about the general health effects associated with each 
    category, and precautions that sensitive groups and the general public 
    can take to avoid exposures of concern, has been made available through 
    an informational booklet, updated as appropriate, that also presents 
    and explains the PSI (EPA, 1994).
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        \2\ Intermediate index values of 200, 300, and 400 were defined 
    and are the basis for the Alert, Warning, and Emergency episode 
    levels included in 40 CFR part 51, appendix L, as part of the 
    Prevention of Air Pollution Emergency Episodes program. This program 
    requires specified areas to have contingency plans in place and to 
    implement these plans during episodes when high levels of air 
    pollution, approaching the SHL, are in danger of being reached. 
    Changes to this emergency episode program will be proposed in the 
    near future.
        Below an index value of 100, historically an intermediate value 
    of 50 was defined either as the level of the annual standard if an 
    annual standard has been established (for PM10 and 
    SO2), or as a concentration equal to one-half the value 
    of the short-term standard used to define an index value of 100 (for 
    O3 and CO). Coarse or inhalable particulate matter, 
    PM10, refers to particles with an aerodynamic diameter 
    less than or equal to a nominal 10 micrometers.
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        In 1979, we made changes to the AQI, in part to reflect revisions 
    to the NAAQS for O3, and to establish requirements for AQI 
    reporting (44 FR 27598). The requirement for State and local agencies 
    to report the AQI appears in 40 CFR part 58.50, and the specific 
    requirements (e.g., what to report, how to report, reporting frequency, 
    calculations) are in appendix G to 40 CFR part 58.
    
    C. What Programs Are Related to the AQI?
    
        Historically, State and local agencies have used primarily the AQI, 
    or other AQIs, to provide general information to the public about air 
    quality and its relationship to public health. In recent years, many 
    States and local agencies, as well as EPA, have been developing new and 
    innovative programs and initiatives to provide more information to the 
    public, in a more timely way. These initiatives, including real-time 
    data reporting through the Ozone Mapping Project and community action 
    programs, can serve to provide useful, up-to-date, and timely 
    information to the public about air pollution and its effects. Such 
    information will help individuals take actions to avoid or reduce 
    exposures of concern and can encourage the public to take actions that 
    will reduce air pollution on days when levels are projected to be in 
    air quality categories of concern to local communities. Thus, these 
    programs are significantly broadening the ways in which State and local 
    agencies can meet the nationally uniform AQI reporting requirements, 
    and are contributing to State and local efforts to provide community 
    health protection and to attain or maintain compliance with the NAAQS. 
    We and State and local agencies recognize that these programs are 
    interrelated with AQI reporting and with the information on the effects 
    of air pollution on public health that is generated through the 
    periodic review, and revision when appropriate, of the NAAQS.
        The most recent revisions to the O3 and PM NAAQS, the 
    Ozone Mapping Project, and community action programs are discussed 
    briefly below. In light of the interrelationships among these programs, 
    we have developed today's revisions to the uniform AQI with the goal of 
    creating a revised AQI that can effectively serve as a nationally 
    uniform link across these programs. In so doing, we intend to support 
    and encourage State and local participation in real-time data reporting 
    initiatives and the development and implementation of community action 
    programs that serve public education and health protection goals.
    1. Ozone and Particulate Matter NAAQS Revisions
        On July 18, 1997, we revised the primary NAAQS for O3 
    and PM based on a thorough review of the scientific evidence linking 
    exposures to ambient concentrations of these pollutants to adverse 
    health effects at levels allowed by the previous NAAQS. In particular, 
    we replaced the 1-hour O3 NAAQS with an 8-hour O3 
    NAAQS and supplemented the PM NAAQS with 24-hour and annual standards 
    for fine particulate matter (measured as 
    PM2.5 3). These decisions were challenged in the 
    U.S. Court of Appeals for the District of Columbia Circuit, and on May 
    14, 1999, the Court remanded them to the Agency for further 
    consideration, principally in light of constitutional concerns 
    regarding section 109 of the Act as interpreted by EPA. American 
    Trucking Associations v. EPA, Nos. 97-1440, 97-1441 (D.C. Cir. May 14, 
    1999). On June 28, 1999, the U.S. Department of Justice on behalf of 
    EPA filed a petition for rehearing seeking review of the Court's 
    decision by the entire Court of Appeals. The EPA is continuing to 
    assess what further legal or administrative proceedings may be 
    appropriate in response to the Court's decision, as well
    
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    as its relevance to other rulemakings such as this one.
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        \3\ PM2.5 refers to particles with an aerodynamic 
    diameter less than or equal to a nominal 2.5 micrometers.
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        With respect to the present rulemaking, we have concluded that it 
    is appropriate to proceed with final action on the proposed AQI 
    revisions. As indicated previously, section 319 of the Act requires the 
    Agency to establish a uniform air quality index, and this requirement 
    is independent of the statutory provisions governing establishment and 
    revision of the NAAQS. Moreover, there is no statutory requirement that 
    the AQI be linked to the NAAQS, although EPA has used NAAQS levels in 
    the past as reference points for the establishment of specific 
    breakpoints within sub-indices. Nothing in the Court's opinion alters 
    the conclusions EPA reached in revising the air quality criteria for PM 
    and O3 under section 108 of the Act, or in the NAAQS 
    rulemakings, concerning the occurrence of specific health effects at 
    varying concentrations of PM and O3 in the air. Regardless 
    of the outcome of the remand as to the NAAQS themselves, we believe the 
    scientific record and conclusions underlying them are more than 
    sufficient as a basis for decisions on the levels at which the public 
    should be notified about health risks associated with daily air 
    quality.4
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        \4\ Under section 319, the levels that are appropriate for this 
    purpose do not necessarily depend on the NAAQS levels that may be 
    appropriate under section 109. Depending on how the Agency chose to 
    set an ambient standard, for example, it might conclude that the 
    standard does not need to preclude certain effects falling below the 
    level of public health concern, and at the same time set the AQI in 
    such a way as to assure that sensitive individuals who might 
    experience those effects receive notification and advice on actions 
    they might take to avoid them. Similarly, AQI values might be set 
    that are higher than the standard would permit but that would 
    require more serious health warnings. This is not to say, however, 
    that the levels of the 1997 NAAQS are irrelevant to decisions on the 
    AQI breakpoints. To the contrary, the levels of the 1997 NAAQS are 
    useful surrogates for a series of scientific conclusions reached in 
    the NAAQS rulemakings, based on the revised air quality criteria, 
    regarding the nature, extent, and severity of health effects 
    associated with varying concentrations of PM and O3 in 
    the air. Accordingly, later sections of this notice make reference 
    as appropriate to relevant levels of the 1997 NAAQS.
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        We do not regard this notification function as involving the 
    constitutional concerns raised in the Court's opinion. The AQI has no 
    bearing on pollution control requirements for specific sources; nor 
    does it serve to implement the NAAQS involved in the litigation. 
    Rather, it provides information on air quality and health that will 
    help individual citizens take prudent, self-protective actions to avoid 
    or reduce exposures of concern and to avoid contributing to air 
    pollution on days when unhealthy air quality is projected. In this 
    regard, the AQI is essentially a way of conveying scientific/medical 
    advice to the public in an easily understood form.
        As indicated below, there was broad support in public comments for 
    modifying and expanding the use of the AQI to take into account the 
    expanded understanding of air quality-health relationships that 
    resulted from EPA's review of the latest scientific information on the 
    effects of PM and O3. Other proposed revisions were designed 
    to enhance the effectiveness of the AQI generally. The function the AQI 
    serves of conveying to the public information on daily air quality and 
    associated health risks is clearly important, and the season of higher 
    pollution levels is imminent. For all the above reasons, we see no 
    reason to delay final action on the proposed revisions of the AQI. The 
    remainder of this section discusses aspects of the O3 and PM 
    NAAQS rulemakings as they relate to today's action.
        As a result of the reviews of the scientific information upon which 
    the 1997 NAAQS for O3 and PM are based, an expanded 
    understanding emerged as to the nature of the relationships between 
    exposure to ambient concentrations of these pollutants and the health 
    effects likely to be experienced, especially near the level of the 
    NAAQS. We and the Clean Air Scientific Advisory Committee (CASAC) 
    5 recognized that for these pollutants there may be no 
    thresholds below which health effects are not likely to occur, but 
    rather a continuum of effects potentially extending down to background 
    levels. As ambient concentrations increase, the proportion of 
    individuals likely to experience effects and the seriousness of the 
    health effects increase. Thus, the 1997 standards were not considered 
    risk free. While the standards were intended to protect public health 
    with an adequate margin of safety, in accordance with section 109(b) of 
    the Act, including the health of sensitive groups, exposures to ambient 
    concentrations just below the numerical level of the standards may 
    result in exposures of concern for the most sensitive individuals. 
    Conversely, exposures to ambient concentrations just above the 
    numerical level of the standards are not likely to result in exposures 
    of concern for most healthy people. This expanded understanding is 
    reflected in the forms of the new standards, which allow for multiple 
    days above the numerical level of the standards.
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        \5\ CASAC is a scientific advisory committee established under 
    the Act to review the scientific criteria and standards and to 
    advise the Administrator on revision of the NAAQS, as appropriate.
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        These understandings were also reflected in CASAC's advice to the 
    Administrator during the O3 NAAQS review, urging expansion 
    of the public health advisory system (i.e., a uniform AQI) and 
    communication to the public of the apparent nonthreshold nature of the 
    health effects. More specifically, a number of CASAC panel members 
    recommended ``that an expanded air pollution warning system be 
    initiated so that sensitive individuals can take appropriate `exposure 
    avoidance' behavior'' (Wolff, 1995). Consistent with this advice, in 
    the preamble to the proposed revisions to the O3 NAAQS (61 
    FR 65733-65734), the Administrator requested comment on the usefulness 
    of providing specific health effects information when ambient 
    concentrations are around the numerical level of the standard, the 
    appropriateness of using the AQI to convey such information to the 
    public, the possible addition of two new AQI categories (one just above 
    and one just below the numerical level of the standard) and associated 
    descriptors and levels, as well as related health effects and 
    cautionary statements.
        Broad support for modifying the AQI was received in public comments 
    on this aspect of the O3 NAAQS proposal, as discussed in the 
    final rule establishing revisions to the O3 NAAQS (62 FR 
    38873-38874). Commenters overwhelmingly endorsed expanding the use of 
    the AQI for various reasons, although many expressed concern with the 
    possible category descriptors suggested in the proposal (i.e., 
    ``moderately good'' and ``moderately unhealthful''). Many commenters 
    felt that an expanded AQI could help particularly sensitive people take 
    action to minimize their exposures, and that the AQI could be combined 
    with community action programs to reduce ambient concentrations when 
    the numerical level of the standard was forecasted to be exceeded. Some 
    commenters endorsed increasing the specificity of health and cautionary 
    statements related to the AQI categories. Commenters from State and 
    local agencies encouraged us to develop any approaches to revising the 
    AQI in consultation with them, specifically in the areas of sharing 
    real-time monitoring data, risk communication with the public, and 
    coordination of a national program.
    2. Real-time Data Reporting Initiative (Ozone Mapping Project)
        The Ozone Mapping Project is part of EPA's Environmental Monitoring 
    for
    
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    Public Access and Community Tracking (EMPACT) initiative--a new 
    approach to providing timely environmental information to communities. 
    It is a cooperative effort of the EPA, State and local air pollution 
    control agencies, and regional organizations including the Mid-Atlantic 
    Regional Air Management Association (MARAMA), the Northeast States for 
    Coordinated Air Use Management (NESCAUM), the northeast Ozone Transport 
    Commission (OTC), the Lake Michigan Air Directors Consortium (LADCO), 
    SouthEast States Air Resource Managers (SESARM), and Central States Air 
    Resource Agencies (CenSARA). During the summer of 1998, EPA's Office of 
    Air Quality Planning and Standards assumed coordination of the project.
        The Ozone Map provides simple and timely information about ground-
    level O3. During the 1998 O3 season it was 
    available on EPA's AIRNOW web site (http://www.epa.gov/airnow) and on 
    some local television and news reports. It is an animated contour map 
    that shows concentrations of O3, in categories ranging from 
    good to moderate to varying degrees of unhealthy, based on AQI values, 
    as they develop across the eastern United States. In 1998, the map was 
    created from real-time, hourly O3 data provided by a network 
    of more than 400 air monitoring stations from South Carolina to 
    Wisconsin and Maine. When accessed on a computer, cautionary statements 
    for each category could be displayed by running a cursor over the 
    legend. Also available on the AIRNOW web site were still maps of 
    maximum values and forecasted values, and archived animated maps. In 
    1999, the ozone mapping coverage is being expanded to include 31 States 
    and over 1500 monitors across the eastern and central U.S., and 
    California. In addition, TV weather service providers are planning to 
    carry the Ozone Map and forecasts as part of their traditional weather 
    packages for local TV stations.
        Along with the Ozone Map, the AIRNOW web site contains information 
    about O3 health effects in the ``Health Facts'' section, and 
    emission reduction activities in the ``What You Can Do'' section. It 
    also provides links to real-time data, and community action program web 
    sites, that are maintained by State and local agencies around the 
    country. The goals of the web site are to: (1) Provide real-time air 
    pollution data in an understandable, visual format, (2) provide 
    information about the public health and environmental effects of air 
    pollution, and (3) provide the public with information about ways in 
    which they can protect their health and actions they can take to reduce 
    pollution.
    3. Community Action Programs
        The implementation of community action programs (also referred to 
    as voluntary action programs or episodic emission control programs) is 
    becoming increasingly popular across the country as an innovative 
    approach used to reduce emissions of O3 precursors, CO, and 
    PM. Motivation for implementation of this type of program often stems 
    from local government and business concerns about the NAAQS attainment 
    status of the area and the restrictions, additional controls, and costs 
    associated with being classified as a nonattainment area. Many areas 
    are also motivated by public health concerns and believe that 
    increasing the amount of air quality information available to sensitive 
    populations raises awareness and results in significant health 
    benefits. Specific goals which are usually associated with community 
    action programs include: (1) Educate the public and enhance protection 
    of public health; (2) attain or maintain NAAQS attainment status and 
    the associated economic benefits; (3) meet specific emission reduction 
    targets; and (4) manage/reduce traffic congestion.
        Community action programs are usually voluntary and generally 
    provide multiple steps that the public, business, and industry can take 
    to reduce emissions when higher levels of air pollution are forecast to 
    occur, including in particular transportation-related measures such as 
    trip reduction, postponement of certain activities such as vehicle 
    refueling, and maintenance of cars. The programs emphasize educating 
    the public about the impact of individual activities on local air 
    quality and the basics of air pollution. The educational component of 
    these programs also helps to create a strong link between environmental 
    goals and associated public health benefits.
        Most of these programs are based on the categories of the AQI and 
    make use of the AQI descriptors and related health effects and 
    cautionary statements on action days. By linking action days to the 
    AQI, local control programs hope to alter individual behavior to reduce 
    emissions and to reduce exposures to the population. In addition to 
    reduced pollutant exposure of the general population due to improved 
    air quality, there are other health benefits directly associated with 
    community action programs that can be enhanced by linkage to the AQI. 
    Different population groups are more sensitive to the harmful effects 
    of the different air pollutants included in the AQI, and the revisions 
    to the AQI being adopted today, together with related informational 
    materials, will significantly improve the effectiveness of 
    communications with these groups. Public education, or programs 
    directly targeting these groups, may provide the most significant 
    benefits of a community action program. Forecasting days with elevated 
    pollution levels, and then communicating effectively about air quality 
    and associated health effects, may help these groups selectively limit 
    their outdoor activities and, therefore, limit their potential for 
    exposures of concern.
        We are committed to providing States and local agencies with 
    support in their efforts to meet air quality standards, to inform the 
    public about air quality, and to educate the public about the impacts 
    of air pollution. The revisions to the AQI being adopted today have as 
    a goal the creation of a revised AQI that can effectively serve as a 
    nationally uniform link across the range of programs (e.g., real-time 
    data reporting initiatives, community action programs) that have these 
    functions.
        In support of community action programs, we have developed 
    informational materials related to the AQI, including the health 
    effects and cautionary statements associated with each category and 
    more detailed health effects information (see section II.D.), available 
    on the AIRNOW web site, that State and local agencies may use to 
    enhance their community action programs. Focusing on transportation 
    measures that are often a major component of community action programs, 
    EPA's OMS has developed a report entitled, ``Community Action Programs: 
    Blueprint for Program Design.'' This document describes the major steps 
    needed to put together a successful episodic control program and 
    provides criteria that State and local agencies can use to examine and 
    evaluate their own programs. The report is available from OMS (see 
    Availability of Related Information).
    
    II. Rationale for Final Revisions
    
        In developing the revisions to the AQI that are being adopted 
    today, we sought extensive input from State and local agencies and from 
    the public. We sponsored a workshop with State and local agencies, 
    participated in numerous meetings, prepared and made available a staff 
    draft revision to the AQI sub-index for O3 for use during 
    the 1998 O3 season, and conducted several focus groups 
    across the nation to obtain public input on the effectiveness of draft 
    revisions to the AQI and related O3 maps and informational 
    materials. A
    
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    detailed history of the process leading to the proposal and the 
    rationale for the proposed revisions are described more fully in the 
    December 9, 1998 proposal notice (63 FR 67818-67834). The sub-sections 
    below contain a description of the revisions we proposed, a discussion 
    of the significant comments we received and our responses to them, and 
    a summary of the AQI we are adopting today.
    
    A. What Revisions Did We Propose?
    
        The primary consideration that shaped the proposed revisions was 
    the importance of providing nationally uniform health information 
    associated with daily ambient levels of the air pollutants included in 
    the index, consistent with the requirement of section 319 of the Act 
    for an index to achieve national uniformity in daily air quality 
    reporting. More specifically, the proposed changes to the AQI sub-
    indices for O3 and PM reflected the 1997 revisions to the 
    O3 and PM NAAQS. The proposed general changes to the 
    structure of the AQI were based on the expanded understanding that 
    emerged during the O3 and PM reviews as to the nature of the 
    relationships between exposure to ambient concentrations of these 
    pollutants and the health effects likely to be experienced, 
    consideration of the implications of changes for the other pollutants, 
    and broad input from State and local agencies and the public. The 
    proposed general changes to the AQI, together with related 
    informational materials, were intended to expand the use of the AQI to 
    provide more pollutant-specific health information, especially when 
    ambient concentrations are close to the level of the primary NAAQS.
    1. What Were the Proposed General Changes?
        a. Categories and related descriptors, index values and colors. The 
    AQI currently incorporates the pollutants O3, PM, CO, 
    SO2, and NO2. Index values range from 0 to 500 
    6, and the index is segmented into five categories named by 
    descriptor words that were chosen to characterize the relationship 
    between daily air quality and public health. To reflect better the 
    current understanding of the health effects associated with exposure to 
    these air pollutants, we proposed to revise the AQI categories and 
    descriptors, and to associate specific colors with the categories as 
    shown below in Table 1.
    ---------------------------------------------------------------------------
    
        \6\ For NO2, the index ranges from 200 to 500, since 
    there is no short-term NAAQS for this pollutant.
    
        Table 1.--Proposed Category Index Values, Descriptors, and Colors
    ------------------------------------------------------------------------
          Index values              Descriptor                 Color
    ------------------------------------------------------------------------
    0-50....................  Good..................  Green
    51-100..................  Moderate..............  Yellow
    101-150.................  Unhealthy for           Orange
                               sensitive groups.
    151-200.................  Unhealthy.............  Red
    201-300.................  Very unhealthy........  Purple
    301-500.................  Hazardous.............  Maroon
    ------------------------------------------------------------------------
    
        These proposed changes reflected the addition of a new category 
    above an AQI of 100, created by dividing the current ``unhealthful'' 
    category into two categories.
        When air quality is in the ``unhealthy for sensitive groups'' 
    range, people that are in the sensitive group, whether the sensitivity 
    is due to medical conditions, exposure conditions, or inherent 
    sensitivity, may experience exposures of concern. However, exposures to 
    ambient concentrations in this range are not likely to result in 
    exposures of concern for most healthy people. The descriptor 
    ``unhealthy for sensitive groups'' was chosen to convey this message 
    clearly. Participants in focus groups (SAIC 1998) clearly understood 
    that ``sensitive groups'' does not refer to the general public, 
    indicating that this descriptor effectively communicates the intended 
    health message. This category would include a caution that while 
    perhaps of interest to all citizens, would be of particular interest to 
    individuals and families of individuals who are members of sensitive 
    groups.
        As air quality moves into the ``unhealthy'' range, exposures are 
    associated with an increase in the number of individuals who could 
    potentially experience effects and includes a greater proportion of 
    members of the general public. Based on input received in the 
    development of the proposal, the descriptor ``unhealthy'' appropriately 
    characterizes air quality in this range.
        In addition to an increasing number of exposures of concern, when 
    air quality moves into the ``unhealthy'' range and above, individuals 
    who were affected at lower levels, typically members of sensitive 
    groups, are likely to experience more serious health effects than 
    members of the general public. To reflect this understanding, it is 
    appropriate to convey two messages in the cautionary statements for 
    both the ``unhealthy'' and ``very unhealthy'' categories. One message 
    is directed to members of sensitive groups, and the other is directed 
    to the general public. The use of a distinct cautionary message for 
    members of sensitive groups is entirely consistent with an original 
    goal that the index be based on the relationships between pollutant 
    concentrations and adverse health effects within various groups, e.g., 
    aggravation of disease in people with respiratory disease and incidence 
    of respiratory effects in healthy people. Guidance on pollutant-
    specific cautionary statements related to the categories of the AQI is 
    discussed below in section II.D.
        Consistent with the overarching goal of national uniformity in the 
    reporting of air quality, we proposed that the specific colors listed 
    in Table 1 be associated with each category. While the AQI can be 
    reported without the use of colors (through text and numbers alone), 
    when the index is reported using colors, we proposed to require that 
    only these specified colors be used. Three examples of AQI reports that 
    use color are the color bars that appear in many newspapers, the color 
    scales on State and local agency web sites, and the color contours of 
    the Ozone Map. We participated in many discussions with State and local 
    agencies and associations regarding which specific colors should be 
    associated with the AQI categories, particularly above an index value 
    of 100. These discussions typically were in the context of either the 
    Ozone Mapping Project or community action programs. It was clear that 
    the color associated with a category can be part of the health effects 
    and cautionary message being conveyed. Were various State and local 
    agencies to use different colors to represent the same category, and 
    thus the same level of air quality, it could well send a confusing 
    message about air quality and associated health effects to the public.
        As an alternative to requiring the use of specified colors, we 
    solicited comment on the option of recommending, rather than requiring, 
    the use of these colors when reporting agencies choose to report the 
    AQI in color format. In soliciting comment on this alternative, we 
    sought to allow communities maximum flexibility in AQI reporting, while 
    still preserving a nationally uniform AQI. We, therefore, requested 
    that commenters addressing this issue discuss how this more flexible 
    approach would satisfy the statutory language requiring a nationally 
    uniform AQI if different colors may be used across the nation to 
    represent the same range of air quality.
        b. Reporting requirements. We proposed to change 40 CFR part 58.50 
    to require reporting of the AQI in all
    
    [[Page 42535]]
    
    Metropolitan Statistical Areas (MSAs) 7 with a population 
    over 350,000, instead of all urbanized areas with a population over 
    200,000. This change was proposed for consistency with the other 
    monitoring regulations in part 58, which are or will be based on MSAs. 
    This proposed change would not, however, have a significant impact on 
    who is required to report, since virtually the same number of cities 
    would be covered under the proposed reporting requirement as are 
    covered under the existing requirement.
    ---------------------------------------------------------------------------
    
        \7\ A complete list of MSAs and their boundaries can be found in 
    the Statistical Abstract of the United States (1998).
    ---------------------------------------------------------------------------
    
        Consistent with early input from State and local agencies, we 
    proposed to change the rounding conventions used to calculate index 
    values corresponding to pollutant concentrations at and above the 
    numerical level of the NAAQS to be consistent with the rounding 
    conventions used in defining the NAAQS for each pollutant. This would 
    avoid situations where a health advisory could be issued that describes 
    the air as unhealthy, when in fact the numerical level of the standard 
    has not been exceeded.
        The proposed rule retained the requirements to identify the area 
    for which the AQI is being reported, the time period covered by the 
    report, the ``critical'' pollutant for which the reported AQI value was 
    derived, the AQI value, and the associated category descriptor. 
    Recognizing that many agencies use a color format to report the AQI, 
    the proposed rule added the requirement to report the associated 
    category color if a color format is used. Because different sensitive 
    groups are at-risk from different pollutants, issuing advisories for 
    all sensitive groups who may be affected at AQI values greater than 100 
    clearly improves public health protection. Therefore, the proposed rule 
    encouraged, but did not require, that AQI reports include: appropriate 
    health effects and cautionary statements, all AQI values greater than 
    100, the AQI for sub-divisions of the MSA (if there are important 
    differences in air quality across sub-divisions of the MSA), possible 
    causes for high index values, and the actual pollutant concentrations. 
    These topics were also discussed in our draft ``Guideline for Public 
    Reporting of Daily Air Quality--Pollutant Standards Index (PSI)'' that 
    was made available on the AIRLINKS web site.
        The proposed rule emphasized the importance of forecasting the AQI 
    by specifying that forecasted values should be reported, when possible, 
    but did not require that forecasted values be reported. Given the 
    importance of the O3 sub-index in a large number of MSAs, 
    and the use of an 8-hour averaging time for calculating the 
    O3 sub-index value, forecasting the O3 index 
    value is now more beneficial than before. For a health advisory system 
    to be effective, people need to be notified as early as possible to be 
    able to avoid exposures of concern. Because the O3 sub-index 
    is based on 8-hour O3 averages, forecasting O3 
    concentrations clearly would have increased value in providing 
    cautionary statements to the public. We recognized that many State and 
    local air agencies are already issuing health advisories based on 
    forecasted O3 concentrations. Since we have determined that 
    forecasting would add much to the benefits of AQI reporting, we 
    indicated that we would be making available guidance on starting a 
    forecasting program (EPA 1999b) in an area or MSA where forecasting is 
    not presently done. Included in the document is guidance on using 
    hourly O3 concentrations as predictors for 8-hour averages.
        c. Index name. Many State and local agencies encouraged us to 
    change the name of the PSI to the Air Quality Index, or AQI, since many 
    agencies already use the name AQI when reporting the AQI value to the 
    public. Most participants in the focus groups preferred the name AQI, 
    commenting that it more clearly identified the index as relating to the 
    quality of the air rather than to environmental pollution in general. 
    Based on these considerations, we solicited comment on changing the 
    index name from Pollutant Standards Index (PSI) to Air Quality Index 
    (AQI).
    2. What Were the Proposed Changes to the Sub-Indices?
        To conform to the proposed general changes to the AQI discussed 
    above, and to reflect the recent revisions to the O3 and PM 
    NAAQS, we proposed changes to the sub-indices for O3, PM, 
    CO, and SO2; no conforming changes are necessary for the 
    NO2 sub-index. The proposed sub-indices are summarized below 
    in Table 2, in terms of pollutant concentrations that correspond to 
    breakpoints in the index, and are discussed in the following sections.
    
                                           Table 2.--Proposed Breakpoints for O3, PM2.5, PM10, CO, and SO2 Sub-indices
    --------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                  O3                                        PM
                                        -------------------------------------------------------------------------------------
                 AQI value                                                                     PM2.5, 24-hr     PM10, 24-hr      CO, 8-hr       SO2, 24-hr
                                                      8-hr (ppm)                1-hr (ppm)     (g/    (g/        (ppm)           (ppm)
                                                                                                   m\3\)           m\3\)
    --------------------------------------------------------------------------------------------------------------------------------------------------------
    50.................................  0.07...............................  ..............              15              50               4            0.03
    100................................  0.08...............................            0.12              65             150               9            0.14
    150................................  0.10...............................            0.16           * 100             250              12            0.22
    200................................  0.12...............................            0.20           * 150             350              15            0.30
    300................................  0.40 (1-hr)........................            0.40           * 250             420              30            0.60
    400................................  0.50 (1-hr)........................            0.50           * 350             500              40            0.80
    500................................  0.60 (1-hr)........................            0.60           * 500             600              50            1.00
    --------------------------------------------------------------------------------------------------------------------------------------------------------
    * If a different SHL for PM2.5 is promulgated, these numbers will be revised accordingly.
    
        a. Proposed ozone sub-index. On July 18, 1997, we revised the 
    O3 primary NAAQS to replace the 1-hour standard with a new 
    standard with an 8-hour average at a level of 0.08 ppm and a form based 
    on the 3-year average of the annual fourth-highest daily maximum 8-hour 
    average O3 concentrations measured at each monitor within an 
    area (62 FR 38856-38896). These proposed revisions were based on 
    findings from the most recent review of the NAAQS indicating that the 
    new primary standard will provide increased protection to the public, 
    especially children active outdoors and other sensitive groups, against 
    a wide range of O3-induced health effects, including 
    decreased lung function; increased respiratory symptoms; hospital 
    admissions and emergency room visits
    
    [[Page 42536]]
    
    for respiratory causes, among children and adults with pre-existing 
    respiratory disease such as asthma; inflammation of the lung; and 
    possible long-term damage to the lungs. In setting this standard, we 
    recognized that there is no apparent threshold below which health 
    effects do not occur, that the standard is not risk free, and, thus, 
    that exposures of concern are possible below the numerical level of the 
    standard for some extremely sensitive individuals.
        We proposed to set an index value of 100 equal to the level of the 
    8-hour O3 standard. Recognizing the continuum of health 
    effects, we considered the results of a quantitative risk assessment 
    (Whitfield et al., 1996) in selecting 8-hour O3 
    concentrations to correspond to index values of 50, 150 and 200. Since 
    no human health effects information was available for 8-hour average 
    O3 concentrations at significantly higher levels, we 
    proposed to retain the breakpoints at the upper end of the AQI scale 
    (between the ``very unhealthy'' and ``hazardous'' categories and the 
    SHL which corresponds to the top of the PSI scale of 500) in terms of 
    the existing 1-hour average concentrations.
        These proposed revisions reflect the new 8-hour O3 NAAQS 
    and will in almost all areas result in a more precautionary index than 
    the current 1-hour sub-index. However, we recognized that a very small 
    number of areas in the U.S. have atypical air quality patterns, with 
    very high 1-hour daily peak O3 concentrations relative to 
    the associated 8-hour average concentrations. In such areas, the use of 
    the current 1-hour sub-index may be more precautionary on a given day 
    than the proposed 8-hour sub-index. To allow for the reporting of the 
    more precautionary sub-index value, we proposed to retain the 1-hour 
    sub-index at and above AQI values of 100 and to allow the reporting of 
    the higher of the two O3 sub-index values. Thus, both the 
    new 8-hour and the current 1-hour sub-indices, as shown in Table 2, 
    were included in the proposed appendix G. Since for the large majority 
    of areas the 8-hour sub-index will be more precautionary, we did not 
    propose to require all areas to calculate both sub-index values. 
    Rather, we proposed to allow areas the flexibility to calculate both 
    sub-index values and, when both sub-index values are calculated, to 
    require that the higher value be reported. We specifically solicited 
    comment on this proposed approach.
        b. Proposed PM sub-index. On July 18, 1997, we revised the PM NAAQS 
    by adding a new set of standards for fine particles, or 
    PM2.5, set at levels of 15 g/m\3\ (annual) and 65 
    g/m\3\ (24-hour average) (62 FR 38652-38760). These revisions 
    were based on findings from the most recent review of the PM NAAQS that 
    recently published studies have indicated that serious health effects 
    were more closely associated with the levels of the smaller particle 
    subset of PM10. These health effects include premature 
    mortality and increased hospital admissions and emergency room visits, 
    primarily in the elderly and individuals with cardiopulmonary disease; 
    increased respiratory symptoms and disease in children and individuals 
    with cardiopulmonary disease; decreased lung function, particularly in 
    children and individuals with asthma; and alterations in respiratory 
    tract defense mechanisms. In addition, PM10 standards were 
    retained at the same levels of 50 g/m\3\ (annual) and 150 
    g/m\3\ (24-hour average) to continue to provide protection 
    against health effects associated with the coarse particle subset of 
    PM10, including aggravation of asthma and respiratory 
    infections. To reflect these revisions to the PM NAAQS, we proposed to 
    add a new sub-index for PM2.5, and to make conforming 
    changes to the sub-index for PM10, consistent with the 
    proposed general changes to the AQI. The proposed sub-indices are 
    summarized in Table 2 and discussed below.
        Proposed new PM2.5 sub-index. Consistent with the 
    historical method of selecting breakpoints of the AQI, we proposed to 
    set an index value of 100 at the level of the 24-hour PM2.5 
    NAAQS, 65 g/m\3\, and an index value of 50 at the level of the 
    annual NAAQS, 15 g/m\3\. Also consistent with the basic 
    structure of the AQI, the proposed upper bound index value of 500 
    corresponds to the SHL, established in section 51.16 of the CFR under 
    the Prevention of Air Pollution Emergency Episodes program. The SHL is 
    set at a level that represents an imminent and substantial endangerment 
    to public health. When we propose revisions to the Prevention of Air 
    Pollution Emergency Episodes program, the proposal will include a SHL 
    for PM2.5. In the interim, we proposed to establish a 
    PM2.5 concentration of 500 g/m\3\ to be associated 
    with a PM2.5 index value of 500.
        For intermediate breakpoints in the AQI between values of 100 and 
    500, PM2.5 concentrations were proposed that generally 
    reflect a linear relationship between increasing index values and 
    increasing PM2.5 values. The available scientific evidence 
    of health effects related to population exposures to PM2.5 
    concentrations between the 24-hour NAAQS level and the proposed 
    PM2.5 concentration to be associated with a PM2.5 
    index value of 500 suggest a continuum of effects in this range, with 
    increasing PM2.5 concentrations being associated with 
    increasingly larger numbers of people likely experiencing serious 
    health effects (62 FR 38675; Staff Paper, p. VII-27). The proposed 
    generally linear relationship between AQI values and PM2.5 
    concentrations in this range, rounded to increments of 50 g/
    m\3\ to reflect the approximate nature of such a relationship, is 
    consistent with this evidence.
        Proposed conforming changes to the PM10 sub-index. 
    Consistent with the retention of the levels of the PM10 
    NAAQS, we proposed to retain the PM10 sub-index generally 
    and to add a new breakpoint at an index value of 150 to conform to the 
    proposed additional AQI category. We proposed that this breakpoint be 
    set at a PM10 24-hour average concentration of 250 
    g/m\3\, the mid-point between the breakpoints associated with 
    index values of 100 and 200. We believe that the PM10 sub-
    index, with this conforming change, remains appropriate for the public 
    health protection purposes of the AQI.
        c. Proposed conforming changes to the CO and SO2 sub-
    indices. Since the current AQI sub-indices reflect the current NAAQS 
    for CO and SO2, the only change we proposed for these sub-
    indices was to add a breakpoint to each sub-index at an index value of 
    150 to conform to the proposed additional AQI category. We proposed 
    that these breakpoints be set at concentrations at the mid-points 
    between the breakpoints associated with index values of 100 and 200, 
    consistent with the approach described above for conforming changes to 
    both the 1-hour O3 sub-index and the PM10 sub-
    index. These proposed breakpoints are summarized in Table 2 and will be 
    reviewed in conjunction with the future reviews of the CO and 
    SO2 NAAQS.
    
    B. What Were the Significant Comments and Our Responses?
    
        This section describes the significant comments we received on 
    proposed revisions to the index and our general responses to them. More 
    detailed comment summaries and responses are contained in a Response to 
    Comments Document that is available in the docket (see Addresses).
    1. Comments and Responses on General Changes
        a. Categories and related descriptors, index values and colors. 
    With regard to the proposed changes to the general structure of the 
    index, we received comments that focused on two major
    
    [[Page 42537]]
    
    issues. The first major issue was whether to add a category above or 
    below the standard, or both. In addition, related to that issue were 
    comments about the proposed descriptor for the category we proposed to 
    add above the level of the standard. The second major issue regarded 
    the particular colors, listed in Table 1, we proposed to associate with 
    each category.
        With regard to the general structure of the index, most commenters 
    supported our proposal to add a category above the level of the 
    standard. However, commenters from environmental groups and several 
    States suggested adding a category below the level of the standard to 
    provide additional caution for members of sensitive groups, instead of, 
    or in addition to one above. These commenters expressed the view that 
    the proposed sub-indices, that added a category above the standard, did 
    not sufficiently caution members of sensitive groups about health 
    effects occurring below the level of the standard. Specifically, their 
    comments were in reference only to potential health effects occurring 
    below the 8-hour O3 and 24-hour PM2.5 standards. 
    Regarding health effects below the PM2.5 standard, one State 
    commenter took exception with the statement in the proposal that an 
    additional category below the standard, while perhaps meaningful for 
    O3, would not be an appropriate distinction for the other 
    pollutants in the index. This commenter noted that ``such a distinction 
    would be more imperative for other pollutants, especially for PM where 
    the level of the 24-hour standard may be less protective of sensitive 
    groups than the ozone standard.'' (Docket No. A-98-20, IV-D-19). 
    Agreeing with the importance of cautioning sensitive groups below the 
    level of the 24-hour PM2.5 standard, another commenter noted 
    ``We believe that adding a category below the level of the standard is 
    of particular importance with respect to fine particles.'' (Docket No. 
    A-98-20, IV-D-11). Regarding the O3 sub-index, some of the 
    States and the environmental groups that endorsed adding a category 
    below the level of the standard supported that position by noting that 
    we and CASAC stated that extremely sensitive individuals may be 
    affected down to background levels of O3. One comment from 
    an environmental group noted that:
    
    The CASAC recognized that for O3 and fine particle 
    pollution, ``there are no discernible thresholds below which health 
    effects are not likely to occur in the most sensitive individuals' 
    as it was advising EPA to set new health standards. We agree with 
    CASAC and support the idea of setting ``an expanded air pollution 
    warning system (to) be initiated so that sensitive individuals can 
    take appropriate exposure avoidance behavior,'' however EPA has 
    misrepresented the health threat with the levels it has proposed. 
    (Docket No. A-98-20, IV-D-17).
    
        A State commenter that supported adding a category below the level 
    of the standard observed that adding such a category would be 
    consistent with EPA's conclusion ``that exposures to ambient 
    concentrations just below the numerical level of the standard may 
    result in exposures of concern for the most sensitive individuals.'' 
    (Docket No. A-98-20, IV-D-19).
        We understand and agree with the issues related to communication of 
    risk below the levels of the 24-hour PM2.5 and 8-hour 
    O3 standards. For the PM2.5 sub-index, we have 
    addressed concerns about health effects below the level of the 24-hour 
    PM2.5 standard by revising the PM2.5 sub-index so 
    sensitive groups are cautioned below the 24-hour PM2.5 
    standard. Based on review of the suggested revisions to the 
    PM2.5 sub-index that we received in comments, we believe 
    this approach fully addresses their concerns. The revision is discussed 
    in section II.B.2 below.
        For better communication of health risk below the 8-hour 
    O3 standard, we have addressed the issues raised by 
    commenters by revising the O3 sub-index. We have expanded 
    the ``moderate'' range of the 8-hour O3 sub-index to make it 
    more precautionary. When air quality is in the ``moderate'' range of 
    the 8-hour O3 sub-index, we have provided health effects and 
    cautionary statements, available in our AQI Reporting Guidance document 
    (EPA, 1999a) (discussed in section II.D), that may be used by State and 
    local agencies to caution unusually sensitive individuals below the 
    level of the 8-hour O3 standard. This revision is discussed 
    in section II.B.2 below.
        We do not believe it is necessary or appropriate to change the 
    general structure of the index by adding a new category below the level 
    of the standard to caution extremely sensitive individuals. Based on 
    the concerns of State and local agencies that the addition of two new 
    categories would unduly complicate the index, we are adding just one 
    new category to maintain the degree of simplicity strongly supported by 
    State and local agencies, none of whom advocated the addition of two 
    new categories. As described in section II.A.1 above, we believe that 
    adding a category above the level of the standard makes a distinction 
    that is useful for members of sensitive groups without alarming the 
    general public. As noted by one State commenter:
    
        We are satisfied and support the proposed category index values, 
    descriptors and colors. [We] believe that the Air Quality Index * * 
    * has been a very effective communication tool during the ozone 
    season. It has been our experience that a category above the 
    standard provides the proper communication to the affected 
    populations without alarming or desensitizing others. (Docket No. A-
    98-20, IV-G-04).
    
        Further, given the changes we have made to the PM2.5 
    sub-index, and the expanded ``moderate'' range and the cautionary 
    statements we have made available in guidance for use below the level 
    of the 8-hour O3 standard, we do not believe a category 
    below the level of the standard to caution members of sensitive groups 
    would be an appropriate distinction for any of the pollutants included 
    in the index. We believe that the approach we have adopted retains the 
    simplicity of the index while allowing for more detailed cautionary 
    information to be made available to the public when appropriate.
        With regard to the descriptor ``unhealthy for sensitive groups,'' 
    some commenters expressed the view that this descriptor is misleading 
    because it encompasses a large segment of the population. In addition, 
    they argued, the public will not know that for certain pollutants 
    healthy people, especially healthy children, are members of sensitive 
    groups. Noting that it is prudent policy to assume that most risk 
    communication regarding air quality impacts will be limited to the 
    general descriptors, some of these commenters requested that if we 
    continue to distinguish sensitive groups from the general population, 
    that the descriptor be changed from ``unhealthy for sensitive groups'' 
    to ``unhealthy for children and other sensitive groups,'' so that the 
    public would receive a clear message that children are members of a 
    sensitive group that may be at increased risk from exposure to ozone. 
    (Docket No. A-98-20, IV-D-2, IV-D-4 and IV-D-11). We agree with the 
    view of these commenters, based on the responses of participants in the 
    focus groups, that the public will not know that healthy people, 
    including healthy children, may be at risk when air quality is in the 
    ``unhealthy for sensitive groups'' range. The suggested descriptor, 
    however, is only appropriate for pollutants for which children are a 
    sensitive group. Since the sensitive groups differ from one pollutant 
    to another, and children are only part of the sensitive group for 
    O3, PM2.5 and NO2, this descriptor is 
    not appropriate for the other pollutants. For
    
    [[Page 42538]]
    
    example, the descriptor ``unhealthy for children and other sensitive 
    groups'' would not be appropriate for use in the CO sub-index, where 
    people with heart disease are the group most at-risk. Use of this 
    descriptor when CO levels are above an index value of 100 could lead to 
    confusion about the health effects associated with high levels of CO. 
    Therefore, we do not believe it would be useful or prudent to adopt the 
    descriptor ``unhealthy for children and other sensitive groups.'' To 
    increase public awareness that healthy children are members of the 
    sensitive group for O3, we are adding the requirement that 
    when the AQI value is above 100, reporting agencies include in their 
    published report a statement describing the sensitive group for that 
    particular pollutant. The reporting requirement for pollutant-specific 
    statements describing sensitive groups is discussed below in section 
    II.C.1.b on reporting requirements, and listed in appendix G. We 
    believe that the requirement for agencies to report the pollutant-
    specific statements identifying the groups at risk, when air quality is 
    above an index value of 100, will more effectively communicate the risk 
    associated with specific air pollutants, and thereby better help 
    members of the public reduce personal exposure. To the extent possible 
    with AQI reporting, this requirement will also ensure that the public 
    is informed that children are part of the sensitive group for 
    O3. This requirement will not only improve protection for 
    healthy children, but also healthy adults, the elderly, and people with 
    heart and lung disease. We believe that another good way to address 
    this lack of awareness is to educate the public, and the media and 
    health care professionals that inform the public, about the health 
    effects message associated with the category ``unhealthy for sensitive 
    groups.'' To help accomplish the goal of educating the public, we will 
    be expanding the development of education and outreach materials and 
    activities as described in section II.D below.
        With regard to the colors listed in Table 1, we received comments 
    concerning both the particular colors associated with the different 
    categories and whether specific colors should be required or 
    recommended. The majority of commenters, including most State and local 
    agencies commenting, supported our proposed color scheme. Many of those 
    (commenters that did support it), had used the same or a similar color 
    scheme associated with either community action programs or ozone maps. 
    Commenters that had used the same or a similar color scheme noted that 
    it effectively and appropriately portrayed the full range of local air 
    quality values. On the other hand, some environmental groups and 
    several States commented that the color red should be used for the 
    category just above standard, instead of the color orange that we 
    proposed. Primarily, these commenters expressed the view that the color 
    orange would not send a sufficiently strong message that the standard 
    has been exceeded. In the proposal we indicated that because the color 
    red sends a strong cautionary message, it is most appropriately used 
    when effects are likely to occur in the general population, and when 
    more serious effects are likely in members of sensitive groups. Many of 
    these commenters noted that since up to 30 percent of the population 
    could be considered to be in the sensitive group for O3, 
    when the standard is exceeded the general public should be alerted. 
    These commenters expressed the view that it is appropriate to use the 
    color red just above the level of the standard both to alert the public 
    of potential health risks and to encourage emission reduction actions. 
    An environmental group commented:
    
        While individuals that are sensitive to poor air quality may 
    look at the daily listing in the newspaper or call a message 
    recorded by the state or local air agency, we know from experience 
    that air quality does not receive broad public attention until it is 
    predicted or reaches the level of ``code red.'' At that point, the 
    television and radio media announces that people should restrict 
    outdoor activity and take steps to not add more pollution to the air 
    by carpooling, using less electricity, or using mass transit. 
    (Docket No. A-98-20, IV-D-17).
    
        Another commenter from a State agency noted:
    
        Considering that the definition of sensitive individuals for 
    ozone includes healthy active children and outdoor workers, a clear 
    unambiguous message needs to be sent to the public so that they can 
    respond accordingly. For parents of active children, a message which 
    states that air quality is unhealthy, and displays it using the 
    color red, sends a clear message--even though it may carry with it 
    the risk that individuals not in the sensitive population might also 
    take exposure avoidance measures. Issuing a message that air quality 
    is unhealthy for sensitive individuals and displays it with a code 
    orange runs the risk of having sensitive individuals, or those 
    guiding sensitive individuals (i.e., doctors and parents) not 
    prescribe any avoidance action because of the ambiguity of the 
    message. (Docket No. A-98-20, IV-G-19).
    
        Additionally, these commenters suggested that the color orange be 
    used for the category they wanted us to add below the level of the 
    standard, as described above.
        In considering these comments, we recognize that the NAAQS are set 
    to protect public health with an adequate margin of safety, including 
    the health of sensitive groups. When the standards are met, public 
    health is protected. Exposures to ambient concentrations just above the 
    numerical level of the standards are not likely to result in exposures 
    of concern for most healthy people. This is especially true for the 8-
    hour O3 standard, which has a concentration-based form 
    designed to offer more protection from higher concentrations than from 
    multiple smaller exceedances of the standard. The form of the 8-hour 
    O3 standard allows for multiple days above the level of the 
    standard, provided the 3-year average of the fourth-highest maximum 
    concentrations does not exceed the level of the standard. This means 
    that public health is protected, even when there are multiple days each 
    year when ambient O3 concentrations are above the level of 
    the standard, as long as the standard is met. Therefore, it is 
    inappropriate on any given day to express a high level of concern when 
    air quality just exceeds the level of the standard. Besides sending an 
    inaccurate health effects message by using the color red with the 
    category ``unhealthy for sensitive groups,'' another concern is the 
    potential loss of credibility that could result from repeatedly sending 
    a signal disproportionate to the expected incidence of noticeable 
    symptoms. If this were to happen, the AQI could lose the power to 
    influence people's behavior to protect their health. One commenter from 
    a State agency expressed this concern:
    
        One of our key concerns * * * is that the general public will 
    become ambivalent if we forecasted 20, 30, or more Code Red days 
    over the course of an ozone season. Under this scenario, people may 
    not take adequate precautions to protect themselves when an actual 
    unhealthy level is reached. (Docket No. A-98-20, IV-G-05).
    
        A commenter from another State agency expressed a similar view:
    
        It is important to make sure that this general message is not 
    jeopardized by treating the new 85 ppb, 8-hour standard as the 
    bright line between healthy and unhealthy. The Code Red message will 
    not be considered credible if it is issued between 40 to 60 times a 
    summer in our area. Last year there were 54 days * * * where the 8-
    hour standard was exceeded. (Docket No. A-98-20, IV-G-13).
    
        From the comments we have received and from our focus group 
    research, we believe that the color red sends too strong a message for 
    use in the
    
    [[Page 42539]]
    
    ``unhealthy for sensitive groups category.'' Additionally, based on the 
    comments of State and local agencies that have used the same or a 
    similar color scheme, we believe that the color orange sends an 
    appropriate health message and yet a strong message that the standard 
    has been exceeded. One State commenter noted that their environmental 
    agency:
    
    has been using a green/yellow/orange/red communication system since 
    1993. The media has used the red, orange and yellow air quality 
    codes to convey a ``the air is not clean'' message. In general, the 
    media has used Code Red to convey a message that air pollution is or 
    will be at a near emergency level. Code Orange has connoted ``very 
    dirty.'' Code Yellow has, in general, been used to characterize air 
    pollution as not too bad--but still not clean. (Docket No. A-98-20, 
    IV-G-13).
    
        Another State commenter noted:
    
        We disagree, however, with * * * [the] assertion that the ``Code 
    Orange'' message in the PSI does not adequately protect public 
    health. Our experience * * * has been that the health message can be 
    effectively delivered for Code Orange levels. We have received much 
    feedback from the general public about our ozone action day program, 
    and the resounding message has been: Thank you for this program, I 
    can now plan my day to avoid exposure to high levels of ozone. 
    (Docket No. A-98-20, IV-G-05).
    
        In addition, ozone mapping projects have successfully represented 
    air quality using the full AQI color scheme. In the Ozone Mapping 
    Project, described in section I.C.2, the proposed AQI color scheme was 
    used successfully during the 1998 O3 season. Participating 
    State and local agencies and regional organizations have selected the 
    same color scheme for use in the 1999 O3 season. Having used 
    the proposed color scheme in their local O3 map, one 
    metropolitan air agency noted that ``EPA's proposed color scheme 
    communicates clearly in a logical progression which in our experience 
    is already understood by the public and the media.'' (Docket No. A-98-
    20, IV-G-11).
        Because we believe the proposed color scheme effectively and 
    appropriately communicates the health effects message that was the 
    basis for setting the O3 and PM standards, we have adopted 
    the color scheme as proposed. However, we strongly agree with the views 
    expressed by commenters that it is important for the health effects 
    message associated with the category ``unhealthy for sensitive groups'' 
    to be effectively communicated to the public, health care providers and 
    the media. It is very important that members of sensitive groups, which 
    for some pollutants includes healthy children and adults, be alerted to 
    potential health risks and that the general public be motivated to take 
    emissions reductions measures when air quality is above the level of 
    the standard. In response to the concerns expressed by these 
    commenters, we are planning to significantly step up the development of 
    education and outreach materials and increase activities to get this 
    message out, as discussed in section II.D below.
        Only two commenters recommended against requiring specific colors. 
    The first commenter did so on the grounds that requiring specific 
    colors would be unenforceable, and may lead to frustration and 
    conflict. While applauding our goal of establishing a consistent 
    message, and agreeing that it is good to have as much national 
    consistency as possible, this commenter noted that efforts to legislate 
    aesthetics are uncomfortable, unwieldy and ultimately unnecessary. 
    (Docket No. A-98-20, IV-D-11). The second commenter noted that some 
    States may elect to use Code Red for ozone action programs at levels 
    other than what is being proposed and the regulation should not 
    preclude them from doing that. (Docket No. A-98-20, IV-D-19). On the 
    other hand, there was very strong support in the comments for us to 
    require that agencies that use color, use specific colors in AQI 
    reporting. All of the other commenters that addressed this issue, 
    including a commenter from an environmental organization, supported 
    requiring specific colors for all State/local agencies using a color 
    format. The commenter from an environmental group noted:
    
        EPA states that revisions to the PSI have as a goal the creation 
    of a nationally uniform link across a range of programs. We urge 
    that this uniformity be achieved through the use of a national 
    public health warning system that is clear to the public. To this 
    end, we do support the EPA requiring that when colors are used by a 
    state in its PSI, that the same color system incorporated in the 
    PSI, and not variants, be utilized by such state. (Docket No. A-98-
    20, IV-D-21).
    
        One of the many State commenters agreeing with us that such a 
    requirement was necessary for national uniformity, noted that 
    ``Specific colors * * * associated with each category should be 
    required for national uniformity and ease of understanding. Anything 
    less would defeat the purpose of a national index for comparing air 
    quality in different locales.'' (Docket No. A-98-20, IV-D-07). Another 
    State commenter made the point that ``Consistency of message is 
    important, especially if the regional nature of many air pollution 
    problems is to be communicated effectively.'' (Docket No. A-98-20, IV-
    D-01).
        In response to the first commenter's objections, we do not believe 
    that requiring specific colors presents any particular enforceability 
    problems. This requirement is one of many contained in the 40 CFR part 
    58 Ambient Air Quality Surveillance requirements and would be 
    enforceable in the same manner and to the same extent as any other 
    requirement of this section. As such, we believe there is no difference 
    in enforceability between this and a requirement for the use of 
    particular descriptors or air quality index values. We expect to work 
    with EPA Regional Offices to ensure that they monitor State 
    implementation of the revised AQI and work with the States to encourage 
    compliance.
        With regard to comments that our requirement would preclude States 
    from using other color schemes and action levels in their voluntary 
    programs, it is important to note that the AQI addresses the reporting 
    of measured air quality and does not impose any requirements or 
    limitations on community action programs based on air quality 
    forecasts. We recognize that a nationally uniform color scheme for AQI 
    reporting will, as a practical matter, complicate a State's efforts to 
    use other color schemes in action programs based on predicted air 
    quality, but they remain free to do so under our regulations.
        Because it is the fundamental goal of the AQI to provide nationally 
    uniform information about daily air quality and the public health 
    messages that are appropriately associated with various daily air 
    quality levels, in a format that is timely and easily understood, we 
    continue to believe that requiring specified colors when the AQI 
    categories are reported in color format is both necessary and 
    appropriate. Neither of the commenters opposing this requirement 
    addressed how a more flexible approach of recommending specific colors, 
    thereby allowing the use of different colors to represent the same 
    range of air quality, would satisfy the statutory language requiring a 
    nationally uniform air quality index. Therefore, we are adopting the 
    requirement, as specified in appendix G below, that when State and 
    local agencies report the AQI in a color format, that the specific 
    colors listed in Table 1 be associated with each category.
        b. Reporting requirements. We received significant comments on 
    several issues related to the reporting requirements, including the 
    population threshold and other aspects of the reporting requirements, 
    the appropriate
    
    [[Page 42540]]
    
    method of monitoring and reporting the PM sub-indices, the effect of 
    AQI changes relative to the SHL program, and the effective date of the 
    final rule. Since we received no significant comments on our proposal 
    to change the rounding conventions for calculating the index to make 
    them consistent with the rounding conventions used in defining the 
    NAAQS, we are adopting that revision as proposed. With regard to the 
    population threshold, one commenter expressed the view that the change 
    from requiring AQI reporting in urbanized areas with a population 
    greater than 200,000, to requiring reporting in MSAs with populations 
    greater than 350,000, would raise the threshold for the requirement and 
    appear to mean that large segments of the U.S. population would not 
    have access to AQI reporting. (Docket No. A-98-20, IV-D-03). We have 
    adopted the requirement for AQI reporting in MSAs with populations 
    greater than 350,000 to be consistent with the State/Local Air 
    Monitoring Stations (SLAMs) monitoring regulations in 40 CFR part 58, 
    since AQI reporting is based on information from SLAMS monitors that 
    are located and reported within the context of MSAs. The use of MSAs 
    also provides for more stable reporting areas since MSAs are usually 
    defined by county boundaries that typically do not change, whereas the 
    boundaries for urbanized areas are very irregular, may include parts of 
    counties, and may change with each census. In selecting the MSA 
    population threshold of 350,000, we tried to make the new reporting 
    requirement equivalent to the old one. Under the new requirement, 
    virtually the same number of cities will be required to report the AQI 
    as were previously. Because urbanized areas and MSAs are not 
    equivalent, we realize that some areas will be required to report the 
    AQI that were not required to do so before this rulemaking, and vice 
    versa. The regulation does not preclude any area from reporting the 
    AQI, and we encourage State and local air agencies to report the AQI 
    whenever possible so that people will be informed about local air 
    quality.
        Another commenter noted that some MSAs fall within the boundaries 
    of more than one State, and requested that we identify which of the two 
    or more reporting agencies would be responsible for reporting the AQI 
    for the MSA. (Docket No. A-98-20, IV-G-15). We expect that decisions 
    about AQI reporting in multi-State MSAs will be made by participating 
    agencies in the same manner as decisions about activities to implement 
    the standards through the State Implementation Plans (SIPs). Guidance 
    for air quality planning and implementation in MSAs that fall within 
    the boundaries of more than one State generally calls for the 
    participating State and local agencies to identify, in the SIPs for 
    those States, who will be responsible for the preparation and 
    submission of the required elements, including AQI reports. Where a 
    local or regional planning organization has been designated to carry 
    out such requirements, such an organization is the appropriate one to 
    report the AQI. In any case, we encourage AQI reporting on the sub-MSA 
    level, especially where the AQI differs within the MSA.
        Another commenter urged us to expand the requirement for AQI 
    reporting to areas with populations less than 350,000, if these areas 
    are likely not to be in attainment for the 8-hour O3 
    standard. To support this position, the commenter noted that 
    O3 can be transported long distances downwind from where it 
    is generated, resulting in serious air quality problems in downwind 
    rural and smaller urban areas. (Docket No. A-98-20, IV-G-27). We agree 
    with this commenter that downwind areas may be significantly affected 
    by transport of O3 and precursors. In section 5 of appendix 
    G, we encourage States to evaluate air quality in affected areas 
    downwind of MSAs to identify the potential for significant transport-
    related air quality impacts and to expand their AQI reporting to 
    address these situations. We have also changed the language in this 
    section such that the affected area need not be contiguous to the 
    reporting MSA.
        On a related topic, one commenter noted an example in which a MSA 
    with a population greater than 350,000, has not registered AQI values 
    in excess of 50 (such that AQI reporting would be discretionary), 
    although values above 100 are registered infrequently at a national 
    monument within the larger air basin. (Docket No. A-98-20, IV-G-17). 
    This commenter requested that we revise the reporting requirements to 
    add an air quality consideration to the population threshold as a 
    second component of AQI reporting. To address one part of this comment, 
    we encourage State and local air agencies to report the AQI and issue 
    forecasts for national parks or monuments whenever possible, since 
    these are places people go to for activities that often involve 
    prolonged or vigorous exertion, thereby increasing the risk from air 
    pollution. We have worked with the National Park Service to develop 
    appropriate guidance for visitors and staff to use when index values 
    are expected to be above 100 for O3. To address the other 
    part of this comment, section 8 of appendix G describes exceptions 
    under which AQI reporting becomes discretionary, either for one 
    pollutant or the entire index, for areas with good air quality. 
    Regarding these exceptions, a State commenter suggested that we require 
    a minimum of 2 years at an AQI value lower than 50 before allowing 
    agencies to ``opt out'' of reporting the AQI for a particular 
    pollutant, so that for example, one unusually good O3 season 
    would not make it possible for an agency to avoid reporting high index 
    values in subsequent O3 seasons. (Docket No. A-98-20, IV-D-
    06). We believe that requiring 2 years of index values lower than 50 
    before allowing State and local agencies discretion in reporting, while 
    appropriate in some situations, may be unnecessary in others. We agree 
    with this commenter that it is appropriate to require reporting of 
    higher index values, even if air quality has been good throughout the 
    previous year. Therefore, we have revised section 8 of appendix G, such 
    that when the criteria for an exemption are no longer met, the 
    responsible agency is required to report the AQI. Another commenter 
    expressed the view that we should strengthen the minimum notification 
    requirements, so that when the AQI value exceeds 100, State and local 
    agencies are required to report the index to all three media (print, 
    radio and television) to help ensure that the public is informed that 
    the standard has been exceeded. (A-98-20, IV-E-3) We agree that it is 
    important to inform the public when the AQI is above 100, and therefore 
    have strengthened the reporting provisions in section 6 of appendix G. 
    In particular, when the AQI exceeds 100, reporting agencies should 
    expand reporting to all major news media, and at a minimum, should 
    include notification to the media with the largest market coverages for 
    the area in question.
        Looking at these reporting provisions more broadly, we believe that 
    it would be very beneficial for reporting agencies to educate the media 
    about alternative sources for this information, such as web sites and 
    community action programs. Many State and local agencies have web sites 
    that provide quick access to timely and accurate air quality and 
    related information. For State and local agencies participating in the 
    Ozone Mapping Project, the media could be directed to the AIRNOW web 
    site as a source of information about O3 air quality and 
    associated health effects for yesterday, today and tomorrow. In 
    addition, this web site provides in-depth information about 
    O3 health effects, sources of emissions and simple
    
    [[Page 42541]]
    
    measures people can take to improve air quality. Community action 
    programs also provide timely and accurate information, and are often 
    used to inform the public when air quality is predicted to be above an 
    index value of 100. Tools and programs such as these can significantly 
    improve the timeliness of AQI reporting and provide additional useful 
    information. We believe that, in the near future, the AQI will be 
    reported by the regional and national media in ways, such as the Ozone 
    Map, that will not be limited to specific MSAs. This type of approach 
    will help provide AQI reporting for areas that would otherwise not be 
    covered, including, in some cases, rural and small urban areas and 
    national parks.
        Regarding reporting the PM sub-indices, one commenter requested 
    that we clarify whether PM2.5 and PM10 should be 
    treated as one pollutant (e.g., reported simply as PM) or two different 
    pollutants (e.g., reported separately). (Docket No. A-98-20, IV-D-19). 
    We expect State and local air agencies to report PM2.5 and 
    PM10 separately, since there are two separate sub-indices 
    with different sensitive groups, and different health effects and 
    cautionary statements. In response to this comment, we have added 
    clarifying language to section 9 in appendix G. In addition, many 
    commenters noted that at the present time there is very little 
    monitoring for PM (both PM2.5 and PM10) that is 
    suitable for use in daily AQI reports, and requested guidance for the 
    use of non-reference methods for the purpose of AQI reporting. Since PM 
    is often measured at intervals longer than every 24-hours, State and 
    local agencies are encouraged to use monitoring data from continuous PM 
    monitors for use in AQI reporting, whenever possible. As noted by 
    commenters, due to the lack of appropriate monitoring information, at 
    this time it may not be possible to report the AQI for PM in many 
    locations. To assist State and local agencies in the use of non-
    reference methods, we have added language to section 10 of appendix G 
    stating that non-reference methods may be used for the purpose of AQI 
    reporting if it is possible to demonstrate a simple linear relationship 
    between the non-reference and the reference methods.
        Regarding the effect of changes to the AQI on the SHL program, we 
    received two significant comments. One commenter noted that our 
    proposed changes to the categories, to standardize them such that the 
    upper bound falls on an even number, rounded to 50 (e.g., 200), and 
    lower bound falls on an odd number (e.g., 201), resulted in the AQI 
    breakpoint of 200 being the upper bound of the ``unhealthy'' category, 
    rather than the lower bound of the ``very unhealthy'' category, as it 
    has been historically. Since the AQI breakpoint of 200 is also commonly 
    used as the ``Alert Level,'' or the first stage of an air pollution 
    emergency episode in example guidance associated with the SHL program, 
    this commenter requested that we leave the AQI value of 200 as the 
    lower breakpoint of the ``very unhealthy'' category, so that emergency 
    episodes would start when air quality is classified as ``very 
    unhealthy'' and include appropriate-sounding health effects and 
    cautionary statements. (Docket No. A-98-20, IV-D-22). We are adopting 
    the breakpoints as proposed, because we believe that it is important to 
    be consistent in the treatment of the category boundaries (e.g., 51 to 
    100, 101 to 150, 151 to 200, etc.). When we propose revisions to the 
    requirements of the SHL program, we plan to change all references to 
    the ``Alert Level'' so they will refer to air quality that exceeds the 
    ``Alert Level,'' rather than to air quality that reaches the ``Alert 
    Level.'' However, State and local agencies should not change their 
    emergency episode plans at this point simply because we are adopting 
    this consistent approach to setting AQI breakpoints. Eventually, some 
    agencies may have to revise emergency episode plans because we have 
    revised the AQI value of 200 for the 8-hour O3 sub-index. 
    But we do not expect States to make any revisions to their emergency 
    episode plans until we promulgate the revised requirements. Finally, 
    several commenters noted that in the proposal, we did not specify an 
    effective date for the final revisions. Some of these commenters 
    suggested that we extend the effective date, with suggestions ranging 
    from 60 days to more than a year after publication. We are adopting an 
    effective date of 60 days after publication. We believe that this will 
    allow adequate time for State and local agencies to revise daily AQI 
    reports. We recognize that it may take longer to revise related 
    informational materials, such as printed documents, or related programs 
    that agencies may want to revise. However, since this rulemaking 
    applies only to the requirements for daily reporting of air quality, we 
    believe an effective date of 60 days is adequate.
        c. Index name. All commenters that expressed a view on the index 
    name supported changing the name of the index from the Pollutant 
    Standards Index (PSI) to the Air Quality Index (AQI), because this name 
    clearly identifies the index as relating to the quality of the air. 
    Accordingly, we are changing the name of the index to the Air Quality 
    Index, or AQI.
    2. Comments and Responses on Changes to the Sub-Indices.
        All of the comments we received on proposed changes to the sub-
    indices focused on the sub-indices that were added for O3 
    (8-hour) and PM2.5. Since we did not receive specific 
    comments on the conforming changes we proposed to the CO, 
    SO2 and PM10 sub-indices, we are adopting these 
    sub-indices as proposed.
        a. Ozone sub-index. We received significant comments on two issues 
    related to the O3 sub-index. The first group of comments was 
    in response to our request for comment on retaining the 1-hour 
    O3 sub-index in addition to the 8-hour O3 sub-
    index. The second group of comments focused on the appropriateness of 
    providing precautionary language below the level of the 8-hour 
    O3 standard. Regarding the 1-hour sub-index, almost all of 
    the comments that addressed this issue supported retaining the 1-hour 
    O3 sub-index. However, one State commenter expressed the 
    view that the proposal was unclear regarding how areas that have not 
    attained the 1-hour O3 standard are to use the new 8-hour 
    O3 sub-index. This commenter also noted that it might be 
    confusing to report the AQI based on the 8-hour O3 sub-index 
    in an area where the 1-hour O3 standard had not yet been 
    attained. (Docket No. A-98-20, IV-D-07). We are requiring that all 
    State and local agencies that report the AQI for O3 
    calculate the 8-hour O3 sub-index, even if the reporting 
    area has not attained the 1-hour standard. In addition to calculating 
    the 8-hour O3 sub-index, which is required, the reporting 
    agency may also calculate the 1-hour O3 sub-index, but this 
    is not required. However, if the reporting agency calculates both 
    O3 sub-index values, it is required to report the higher 
    index value of the two. The AQI does not relate to attainment status; 
    rather, it is a tool for reporting daily air quality and associated 
    health information. We are retaining the 1-hour O3 sub-index 
    only because we recognize that there are a very small number of areas 
    in the U.S. that have atypical air quality patterns, with very high 1-
    hour daily peak O3 concentrations relative to 8-hour average 
    concentrations. In such areas, an index value greater than 100 might be 
    calculated using the 1-hour sub-index, even when the 8-hour sub-index 
    might be below 100. For these areas, the use of the 1-hour sub-index is 
    clearly more precautionary. Because our major interest is that 
    appropriate precautionary messages be issued, we
    
    [[Page 42542]]
    
    are not retaining a complete 1-hour O3 sub-index with 
    ``good'' and ``moderate'' categories. Likewise, when ambient 8-hour 
    O3 concentrations are greater than 0.374 ppm, reporting 
    agencies must calculate the index value using the 1-hour O3 
    sub-index. This is because no human health effects information is 
    available for higher 8-hour average O3 concentrations to use 
    as a basis for selecting 8-hour breakpoints and for developing 
    appropriate health effects and cautionary statements. We believe that 
    since State and local agencies are required to report the name of the 
    pollutant responsible for an index value greater than 100, but not the 
    associated averaging period, using the 8-hour O3 sub-index 
    should not be confusing in areas that have not yet attained the 1-hour 
    O3 standard.
        Regarding the issue of alerting sensitive individuals below the 
    level of the 8-hour O3 standard, some commenters not only 
    suggested adding a category below the level of the standard, but also 
    suggested reducing the lower bound of the ``moderate'' category. 
    (Docket No. A-98-20, IV-D-11, IV-D-17, IV-D-19, IV-G-21). We are not 
    adding a category below the level of the standard as discussed in 
    section II.B.1. above. However, to be somewhat more precautionary, we 
    have expanded the ``moderate'' range by reducing the lower bound of 
    this category from 0.070 ppm to 0.065 ppm O3, 8-hour 
    average. We believe that setting the breakpoint between the ``good'' 
    and ``moderate'' categories at this lower level, is appropriate, based 
    in part on risk estimates done in conjunction with the review of the 
    O3 NAAQS which suggested that risk to healthy people likely 
    becomes negligible at this level (Whitfield et al., 1996). This change 
    is also responsive to comments from State agencies that the proposed 
    range of the ``moderate'' category was so narrow (spanning only 15 ppb 
    O3, as compared to 20 ppb range used in the Ozone Map in 
    1998) that it would be more difficult to forecast accurately and also 
    would provide too quick a transition from good to unhealthy. (Docket 
    No. A-98-20, IV-D-10, IV-G-04). Conversely, an industry group and a 
    State commenter took exception to issuing a ``limited health notice'' 
    for O3 that we proposed as the purpose of the ``moderate'' 
    category. (Docket No. A-98-20, IV-D-12, IV-G-14). The State commenter 
    objected to the use of the term ``health notice'' below the level of 
    the standard because it implies that the standard is not protective of 
    public health. In addition to stating that the ``limited health 
    notice'' associated with moderate air quality is inconsistent with the 
    8-hour O3 standard because the standard is intended to 
    protect public health, even the health of sensitive populations, with 
    an adequate margin of safety, the industry commenter expressed the view 
    that we should omit from our materials the health effects and 
    cautionary statements suggesting that air quality meeting the level of 
    the standard is a threat to health. We agree with the industry and 
    State commenters that since the 8-hour O3 standard is 
    intended to protect public health, including the health of sensitive 
    groups, with an adequate margin of safety, that the term ``limited 
    health notice'' may be misleading. However, we continue to believe that 
    it is appropriate to provide guidance with cautionary language for 
    extremely sensitive individuals, not populations or groups, below the 
    level of the standard. This approach is consistent with the advice of 
    CASAC, and the way we discussed expanding the use of the AQI, 
    specifically to caution extremely sensitive individuals below the level 
    of the O3 standard, in the O3 proposal and final 
    decision notices.
        b. PM2.5 sub-index. We received a number of comments 
    regarding the PM2.5 sub-index, almost all of them focusing 
    on our proposal to set the index value of 100 at the level of the 24-
    hour standard (65 g/m3). Some commenters 
    recommended setting an index value of 100, or otherwise providing for 
    cautionary messages, at concentrations lower than 65 g/
    m3. One commenter, for example, stated that under the 
    proposal ``many areas of the country will likely violate the annual 
    standard of 15 g/m3 without ever (or hardly ever) 
    reaching a PSI of 100 or a category indicating some degree of 
    unhealthfulness. This situation will result in an inconsistent and 
    inappropriate message to the public, especially given the severe health 
    effects associated with fine particles.'' (Docket No. A-98-20, IV-D-
    11).
        In light of these comments, we have reexamined the basis for 
    selecting PM2.5 AQI breakpoints and agree that the sub-index 
    as proposed would not adequately caution sensitive groups about 
    potential risks associated with short-term exposures to 
    PM2.5. This is essentially because the proposed 
    PM2.5 sub-index was developed using the Agency's historical 
    approach to selecting index breakpoints, which on examination does not 
    correspond well with the way the PM2.5 standards were 
    intended to function. The historical practice has been simply to set 
    the AQI value of 100 at the level of the short-term standard for a 
    pollutant (in this case, the 24-hour PM2.5 standard) and the 
    AQI value of 50 at the level of the annual standard, if there is one, 
    or at one-half the level of the short-term standard.8 This 
    method of structuring the index is appropriate for a ``typical'' suite 
    of air-quality standards, which includes a short-term standard designed 
    to protect against the health effects associated with short-term 
    exposures and an annual standard designed to protect against health 
    effects associated with long-term exposures. In such cases, the short-
    term standard in effect defines the level of health protection provided 
    against short-term risks and thus is a useful benchmark against which 
    to compare daily air-quality concentrations.
    ---------------------------------------------------------------------------
    
        \8\ See 63 FR 67819, 67829 (Dec. 9, 1998).
    ---------------------------------------------------------------------------
    
        In the case of the PM2.5 standards, however, EPA took a 
    different approach to protecting against health risks associated with 
    short-term exposures. For reasons discussed in the preamble to the 
    final standards, the annual and 24-hour PM2.5 standards were 
    designed to work together for this purpose, and the intended level of 
    protection against short-term risk is not defined by the 24-hour 
    standard but by the combination of the two standards working in 
    concert. Indeed, the annual PM2.5 level of 15 g/
    m3 was intended to serve as the principal vehicle for 
    protection against short-term PM2.5 exposures (by reducing 
    the entire distribution of PM2.5 concentrations in an area), 
    with the short-term standard serving essentially to provide 
    supplemental protection in special situations. 9 Given the 
    respective roles of the two standards, setting the AQI value of 100 at 
    the level of the 24-hour standard would not reflect the short-term 
    health risks associated with lower concentrations, which the annual 
    standard was designed to address. Accordingly, we agree that it is 
    appropriate to caution members of sensitive groups below the level of 
    the 24-hour standard and believe this should be done in a way that 
    reflects the intended roles of both standards in protecting against 
    short-term risks.
    ---------------------------------------------------------------------------
    
        \9\ See 62 FR 38669-71, 38676-77 (July 18, 1997).
    ---------------------------------------------------------------------------
    
        It would also be inappropriate to compare daily air-quality 
    concentrations directly with the level of the annual standard (by 
    setting the AQI value of 100 at that level), because the annual 
    standard represents an average of many daily concentrations rather than 
    daily values per se. In the circumstances, we believe the guiding 
    principle for PM2.5 should be to set the AQI value of 100 in 
    a way that, at least conceptually, reflects the general level of health 
    protection against short-term risks
    
    [[Page 42543]]
    
    provided by the annual and 24-hour standards in combination. This 
    approach, although inexact, is consistent with the historical approach, 
    in that the underlying logic of that approach, as applied to a typical 
    suite of standards, is also to set the AQI value of 100 in a way that 
    reflects the level of protection provided against short-term risks--
    that is, by setting it at the level of the short-term standard that 
    provides the protection. In the case of PM2.5, as indicated 
    above, the level of the 24-hour standard (65 g/m3) 
    is too high to reflect the intended level of protection, and the level 
    of the annual standard (15 g/m3) is too low. 
    Between the two values, the available health studies indicate a 
    continuum of risks associated with increasing PM concentrations, 
    although with significant uncertainties as to the extent of the risk 
    associated with single peak exposures.10 Consistent with 
    EPA's general practice of setting AQI breakpoints in symmetrical 
    fashion where health effects information does not suggest particular 
    levels,11 we concluded that it is appropriate to set the AQI 
    value of 100 at the mid-point of the range between the annual and the 
    24-hour PM2.5 standards (40 g/m3). Given 
    that decision, we also concluded that it is appropriate to retain the 
    level of the annual standard for an AQI value of 50, as proposed, and 
    to set the AQI level of 150 at the level of the 24-hour standard.
    ---------------------------------------------------------------------------
    
        \10\ See 62 FR 38670, 38677 (July 18, 1997).
        \11\ See 63 FR 67824, 67832 (Dec. 9, 1998).
    ---------------------------------------------------------------------------
    
        To reiterate, the purpose of setting the AQI value of 100 somewhat 
    below the level of the 24-hour standard was to reflect the dual role of 
    the annual and 24-hour PM2.5 standards in protecting against 
    short-term risks, and the aim was to select a breakpoint that would 
    serve as a rough surrogate for the general level of protection provided 
    by the two standards in combination. Given the nature of the standards 
    and the available health information, a more exact approach was not 
    possible. In this regard, setting the breakpoint at the mid-point of 
    the range between the annual and 24-hour standards, as opposed to a 
    level somewhat higher or lower within that range, simply reflected 
    EPA's general practice of setting symmetrical breakpoints as indicated 
    above, and does not imply any sort of health-effects threshold. In 
    particular, it does not reflect a judgment about the extent of the risk 
    associated with single peak concentrations of PM2.5, as to 
    which the available health information is inconclusive, or the level at 
    which EPA might set a 24-hour standard if the annual standard did not 
    serve as the primary vehicle for protection against such 
    concentrations. As with other AQI breakpoints, it also has no effect on 
    the degree of control required of specific sources.
        In short, EPA's decision to treat the annual standard as the 
    principal vehicle for protecting against short-term PM2.5 
    concentrations, although judged to be the best approach based on the 
    available health information, does present a different situation than 
    that involved in previous AQI rulemakings. As discussed in the preamble 
    to the final standards, the annual standard was intended to reduce all 
    PM2.5 concentrations, including short-term peaks, in an area 
    sufficiently to protect public health with an adequate margin of 
    safety, aside from special situations which the 24-hour standard was 
    designed to address. As one commenter suggested, however, it would be 
    possible for an area to violate the annual standard without ever 
    experiencing (or seldom experiencing) daily peaks that exceeded the 
    level of the 24-hour standard. Moreover, it might be difficult, if not 
    impossible, to predict in advance whether the annual standard will be 
    attained in a given area. For these reasons, as well as the 
    uncertainties in the available health information, it is inherently 
    difficult to judge the significance of single peak concentrations when 
    they occur. In view of the various uncertainties involved, particularly 
    sensitive individuals may wish to avoid exposure to such 
    concentrations, especially concentrations that approach the level of 
    the 24-hour standard. To facilitate such choices, consistent with the 
    purposes of the AQI and the advice of CASAC, we believe that cautioning 
    members of sensitive groups in the range of 40 to 65 g/
    m3 is appropriate.
        We did not receive any comments on the proposal to establish a 
    concentration of 500 g/m3 to be associated with a 
    PM2.5 index value of 500, or our method of selecting the 
    intermediate breakpoints. Therefore, we are adopting 500 g/
    m3 as the upper bound of the index.12 For 
    intermediate breakpoints in the AQI between values of 150 and 500, we 
    have adopted PM2.5 concentrations that generally reflect a 
    linear relationship between increasing index values and increasing 
    PM2.5 values. As discussed in the proposal, the generally 
    linear relationship between AQI values and PM2.5 
    concentrations in this range, rounded to increments of 50 g/
    m3 to reflect the approximate nature of such a relationship, 
    is consistent with the health effects evidence that was the basis for 
    the PM standards.
    ---------------------------------------------------------------------------
    
        \12\ As discussed in the proposal, should the final SHL for 
    PM2.5, when promulgated, be different from this 
    concentration, we will revise this PM2.5 sub-index 
    accordingly.
    ---------------------------------------------------------------------------
    
    C. What Are the Final Revisions?
    
        The sub-sections below only summarize changes to the regulatory 
    text. They do not describe all aspects of 40 CFR part 58.50 or appendix 
    G.
    1. What Are the General Changes?
        Based on the proposed structure of the AQI, the comments we 
    received and our responses to them, as discussed above, we are adopting 
    the following changes to the general structure and reporting 
    requirements to the AQI.
        a. Categories and related descriptors, index values and colors. We 
    are adopting the index values, descriptors and associated colors listed 
    in Table 1 above.
        b. Reporting requirements. We are revising 40 CFR 58.50 to require 
    reporting of the AQI in all MSAs with a population over 350,000. In 
    appendix G, we are adopting rounding conventions to be used to 
    calculate index values that are consistent with the rounding 
    conventions used in defining the NAAQS for each pollutant.
        The final rule retains the requirements to identify the area for 
    which the AQI is being reported, the time period covered by the report, 
    the ``critical'' pollutant for which the reported AQI value was 
    derived, the AQI value, and the associated category descriptor. The 
    final rule adds two requirements: (1) To report the associated category 
    color if a color format is used and, (2) to report the pollutant-
    specific sensitive group for any reported index value greater than 100. 
    The final rule encourages, but does not require, that AQI reports 
    include: appropriate health effects and cautionary statements, all AQI 
    values greater than 100, the AQI for sub-divisions of the MSA (if there 
    are important differences in air quality across sub-divisions of the 
    MSA), possible causes for high index values, and the actual pollutant 
    concentrations.
        In the case of rural or small urban areas that are significantly 
    affected by pollutants transported from a MSA where the AQI is 
    reported, the final rule recommends that the MSA report the AQI for the 
    affected areas as well. In addition, when the AQI is greater than 100, 
    reporting agencies should expand AQI reporting to include all major 
    news media. The final rule continues to allow agencies to discontinue 
    reporting for any pollutant, if index values for that pollutant have 
    been below 50 for an entire season or a year. However, if in subsequent 
    years pollutant levels rise
    
    [[Page 42544]]
    
    such that index values for that pollutant would be above 50, then the 
    final rule requires that AQI reporting for that pollutant resume. The 
    final rule emphasizes the importance of forecasting the AQI by 
    specifying that forecasted values should be reported, when possible, 
    but does not require that forecasted values be reported.
        c. Index name. We are adopting the name the Air Quality Index or 
    AQI.
    2. What Are the Changes to the Sub-Indices?
        Based on the proposed sub-indices, the comments we received and our 
    responses to them, as discussed above, we are adopting new sub-indices 
    corresponding to the 8-hour O3 standard and the 
    PM2.5 standards, as well as conforming changes to the CO, 1-
    hour O3, PM10, and SO2 sub-indices. 
    The adopted breakpoints for the O3 (8-hour and 1-hour) 
    PM2.5, PM10, CO and SO2 sub-indices 
    are listed in Table 3.
    
                                               Table 3.--Breakpoints for O3, PM2.5, PM10, CO, and SO2 Sub-indices
    --------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                  O3                                        PM
                                        -------------------------------------------------------------------------------------
                 AQI value                                                                     PM2.5, 24-hr     PM10, 24-hr   CO, 8-hr (ppm)    SO2, 24-hr
                                                      8-hr (ppm)                1-hr (ppm)     (g/    (g/                        (ppm)
                                                                                                    m3)             m3)
    --------------------------------------------------------------------------------------------------------------------------------------------------------
    50.................................  0.06...............................  ..............              15              50               4            0.03
    100................................  0.08...............................            0.12              40             150               9            0.14
    150................................  0.10...............................            0.16              65             250              12            0.22
    200................................  0.12...............................            0.20           * 150             350              15            0.30
    300................................  0.40 (1-hr)........................            0.40           * 250             420              30            0.60
    400................................  0.50 (1-hr)........................            0.50           * 350             500              40            0.80
    500................................  0.60 (1-hr)........................            0.60           * 500             600              50           1.00
    --------------------------------------------------------------------------------------------------------------------------------------------------------
    * If a different SHL for PM2.5 is promulgated, these numbers will be revised accordingly.
    
        These sub-indices are presented in more detail in appendix G to 
    reflect the changes to the numerical rounding conventions for 
    calculating index values.
    
    D. What Are the Related Informational Materials?
    
        The primary documents associated with the AQI and this rulemaking, 
    are our guidance on AQI reporting, ``Guideline for Public Reporting of 
    Daily Air Quality--Air Quality Index (AQI)'' (EPA 1999a), and our 
    guidance on AQI forecasting, ``Guideline for Developing an Ozone 
    Forecasting Program'' (EPA 1999b). These documents are available on 
    AIRLINKS (http://www.epa.gov/airlinks). The AQI Reporting document 
    contains information regarding the AQI requirements and 
    recommendations, example AQI reports, and a list of MSAs required to 
    report the AQI. It also includes pollutant-specific health effects and 
    cautionary statements for use with the index, for O3, 
    PM2.5, PM10, CO, and SO2. The AQI 
    Forecasting document explains the steps necessary to start an air 
    pollution forecasting program. Included in the document is guidance on 
    using hourly O3 concentrations as predictors for 8-hour 
    averages.
        Other related informational materials are also available. The 
    brochure ``The Pollutant Standards Index'' (EPA 1994) contained general 
    information about the health effects and air quality, and general 
    precautions that sensitive groups and the general public can take to 
    avoid exposures of concern. It is being revised to be consistent with 
    the new name (i.e., the Air Quality Index brochure), with final 
    revisions to the AQI, and will identify sensitive groups in the health 
    effects statements for each of the pollutants, and include the 
    pollutant-specific health effects and cautionary statements discussed 
    above. A colorful fact sheet, called the ``Air Quality Guide,'' 
    provides information about the AQI, O3 health effects and 
    the sources of ground-level O3 is available on the AIRNOW 
    web site. A revised booklet, ``SMOG--Who Does It Hurt?,'' provides 
    information for the general public about O3 health effects 
    and is based on scientific information gained in the recent review of 
    the O3 standard. ``SMOG--Who Does It Hurt?'' was designed to 
    provide, in simple language, enough detail for individuals to 
    understand who is at most risk from O3 exposure and why, the 
    nature of O3 health effects, and a detailed explanation of 
    how individuals can reduce the likelihood of exposure using common 
    everyday activities as examples. We are also developing a shorter, 
    summary pamphlet about O3 health effects to complement the 
    ``SMOG--Who Does It Hurt?'' booklet. We expect the AQI brochure, 
    ``SMOG--Who Does It Hurt?'' and the shorter summary pamphlet about 
    O3 health effects to be available in paper format and on the 
    AIRNOW web site early in the 1999 ozone season. In addition, we will 
    translate the Air Quality Guide, the AQI brochure, ``SMOG--Who Does It 
    Hurt?'', and the shorter summary pamphlet into Spanish. These materials 
    will be available on a Spanish page on the AIRNOW web site.
        There are other materials available on the AIRNOW web site that 
    provide general information about O3. Information about 
    ground-level as contrasted to stratospheric O3 may be found 
    in EPA's publication ``Ozone: Good Up High, Bad Nearby.'' The EPA's 
    video, ``Ozone Double Trouble'' also provides information about ground-
    level and stratospheric O3 and the health effects associated 
    with exposure to ground-level O3, or smog.
        In addition to the products discussed above, to address the 
    concerns of commenters that when air quality is in the ``unhealthy for 
    sensitive groups'' range the public will not understand that the 
    standard has been exceeded or who is at risk, we are going to 
    significantly increase education and outreach related to the AQI. At 
    this point, we are still in the process of planning specific new 
    products or activities, but have decided what general direction these 
    efforts will take. First, we plan to increase our contacts with the 
    news providers to better inform them about the importance of including 
    accurate, timely and understandable information in their broadcasts and 
    reporting, and to enlist them as full partners in the implementation of 
    the AQI. Second, we plan to form new associations with health care 
    providers to keep them informed about air pollution health effects, 
    since these professionals are the most trusted source of health effects 
    information. Third, we plan to increase direct outreach to the public 
    through a variety of means, including materials tailored to school-age 
    children, the Spanish-speaking community, and others. Finally, we plan 
    to work with public health interest organizations to support
    
    [[Page 42545]]
    
    their efforts to provide more immediate and interactive education and 
    outreach to all of these groups.
    
    III. Regulatory and Environmental Impact Analyses
    
    A. Executive Order 12866: OMB Review of ``Significant Actions''
    
        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 ``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
        (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. The EPA has determined that the revisions to air 
    quality index reporting in this final rule would not 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, and therefore did not 
    prepare a regulatory impact assessment. The OMB has advised us this 
    final decision should be construed as a ``significant regulatory 
    action'' within the meaning of Executive Order 12866. Accordingly, this 
    action was submitted to the OMB for review. Any changes made in 
    response to OMB suggestions or recommendations will be documented in 
    the public record and made available for public inspection at EPA's Air 
    and Radiation Docket Information Center (Docket No. A-98-20).
    
    B. Regulatory Flexibility Analysis/Small Business Regulatory 
    Enforcement Fairness Act
    
        Under the Regulatory Flexibility Act (RFA), 5 U.S.C. 601 et seq., 
    EPA must prepare a regulatory flexibility analysis assessing the impact 
    of any proposed or final rule on small entities. Under 6 U.S.C. 605(b), 
    this requirement may be waived if EPA certifies that the rule will not 
    have a significant economic impact on a substantial number of small 
    entities. Small entities include small businesses, small not-for-profit 
    enterprises, and governmental entities with jurisdiction over 
    populations less than 50,000 people.
        Today's final decision to revise the AQI program modifies existing 
    air quality reporting requirements for MSA's with populations over 
    350,000 people. Today's final decision will not establish any new 
    regulatory requirements affecting small entities. On the basis of the 
    above considerations, EPA certifies that today's final decision will 
    not have a significant economic impact on a substantial number of small 
    entities within the meaning of the RFA. Based on the same 
    considerations, EPA also certifies that the new small-entity provisions 
    in section 244 of the Small Business Regulatory Enforcement Fairness 
    Act (SBREFA) do not apply.
    
    C. Unfunded Mandates Reform Act
    
        Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Public 
    Law 104-4, establishes requirements for Federal agencies to assess the 
    effects of their regulatory actions on State, local, and tribal 
    governments and the private sector. Under section 202 of the UMRA, EPA 
    generally must prepare a written statement, including a cost-benefit 
    analysis, for proposed and final rules with ``Federal mandates'' that 
    may result in expenditures to State, local and tribal governments, in 
    the aggregate, or to the private sector, of $100 million or more in any 
    1 year. In addition, before EPA establishes any regulatory requirements 
    that may significantly or uniquely affect small governments, including 
    tribal governments, it must have developed under section 203 of the 
    UMRA a small government agency plan. The plan must provide for 
    notifying potentially affected small governments, enabling officials of 
    affected small governments to have meaningful and timely input in the 
    development of EPA regulatory proposals with significant Federal 
    intergovernmental mandates, and informing, educating, and advising 
    small governments on compliance with the regulatory requirements.
        The EPA has determined that today's final decision would not 
    include a Federal mandate that may result in estimated costs of $100 
    million in any 1 year to either State, local, or tribal governments, in 
    the aggregate, or to the private sector. Accordingly, EPA has 
    determined that the provisions of section 202 of the UMRA do not apply 
    to this rulemaking. With regard to section 203 of the UMRA, EPA has 
    determined that this rule contains no regulatory requirements that 
    might significantly or uniquely affect small governments. This rule 
    requires reporting of the Air Quality Index only in MSAs with 
    populations greater than 350,000, and therefore does not affect small 
    governments.
    
    D. Paperwork Reduction Act
    
        Today's final decision does not establish any new information 
    collection requirements beyond those which are currently required under 
    the Ambient Air Quality Surveillance Regulations in 40 CFR part 58 (OMB 
    #2060-0084, EPA ICR No. 0940.15). Therefore, the requirements of the 
    Paperwork Reduction Act do not apply to today's action.
    
    E. Executive Order 13045: Children's Health
    
        Executive Order 13045, entitled ``Protection of Children from 
    Environmental Health Risks and Safety Risks'' (62 FR 19885, April 23, 
    1997), requires Federal agencies to ensure that their policies, 
    programs, activities, and standards identify and assess environmental 
    health and safety risks that may disproportionately affect children. To 
    respond to this order, agencies must explain why the regulation is 
    preferable to other potentially effective and reasonably feasible 
    alternatives considered by the agency. In today's final decision, EPA 
    identified children as one of the sensitive groups which may be at 
    increased risk of experiencing the effects of concern following 
    exposure to O3, PM2.5 and NO2.5. The 
    AQI categories, descriptors, and health effects and cautionary 
    statements as proposed, for the first time reflect consideration of the 
    increased health risk to children which may result from such exposures. 
    Promulgation of the proposed AQI is one potentially effective 
    alternative that was considered. However, based on comments that the 
    public may not be aware that healthy, active children are included in 
    the sensitive groups for O3, PM2.5 and 
    NO2, we have adopted the additional requirement that 
    reporting agencies must include a pollutant-specific statement of the 
    sensitive groups when an index value of 100 is exceeded. For example, 
    when reporting an AQI value of 110 for ozone, the reporting agency must 
    include a statement that children and people with asthma are the groups 
    most at risk. Whenever the AQI value is above 100 for a pollutant, and 
    children are one of the sensitive groups for that pollutant, the AQI 
    report must include a statement
    
    [[Page 42546]]
    
    that children are at risk. Therefore, today's action does comply with 
    the requirements of E.O. 13045.
    
    F. Executive Order 12848: Environmental Justice
    
        Executive Order 12848 requires that each Federal agency 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 minorities and low-income populations in the United 
    States.
        The nature of today's action is to inform the general public, 
    including minorities and low-income populations, about the nature of 
    the air pollution in the areas in which they live. Today's action 
    establishes a uniform tool for States to use to develop programs which 
    will caution particularly sensitive people to minimize their exposures 
    and educate the public about general health effects associated with 
    exposure to different pollution levels. States may also use information 
    established as part of the AQI to trigger programs designed to reduce 
    emissions to avoid exceedances of the NAAQS. Therefore, today's action 
    will help facilitate public participation, outreach, and communication 
    in areas where environmental justice issues are present.
    
    G. Executive Order 12875: Enhancing Intergovernmental Partnerships
    
        Under Executive Order 12875, EPA may not issue a regulation that is 
    not required by statute and that creates a mandate upon a State, local 
    or tribal government, unless the Federal government provides the funds 
    necessary to pay the direct compliance costs incurred by those 
    governments, or we will consult with those governments. If EPA complies 
    by consulting, Executive Order 12875 requires us to provide to OMB a 
    description of the extent of our prior consultation with 
    representatives of affected State, local and tribal governments, the 
    nature of their concerns, copies of any written communications from the 
    governments, and a statement supporting the need to issue the 
    regulation. In addition, Executive Order 12875 requires us to develop 
    an effective process permitting elected officials and other 
    representatives of State, local and tribal governments ``to provide 
    meaningful and timely input in the development of regulatory proposals 
    containing significant unfunded mandates.''
        Today's rule implements requirements set forth in section 319 of 
    the Act and thus is required by statute. This rule does not establish a 
    wholly new requirement but rather modifies existing reporting 
    requirements which State and local governments have been implementing 
    for approximately 20 years. While these changes are significant in many 
    ways, they are not expected to result in a significant increase in 
    reporting burdens. Nonetheless, EPA engaged in extensive consultation 
    with State and local governments in the development of the proposed and 
    final rules, and this consultation is discussed and documented 
    elsewhere in today's notice and in the notice of proposed rulemaking.
    
    H. Executive Order 13084: Consultation and Coordination With Indian 
    Tribal Governments
    
        Under Executive Order 13084, EPA may not issue a regulation that is 
    not required by statute, that significantly or uniquely affects the 
    communities of Indian tribal governments, and that imposes substantial 
    direct compliance costs on those communities, unless the Federal 
    government provides the funds necessary to pay the direct compliance 
    costs incurred by the tribal governments, or EPA will consult with 
    those governments. If EPA complies by consulting, Executive Order 13084 
    requires us to provide to OMB, in a separately identified section of 
    the preamble to the rule, a description of the extent of our prior 
    consultation with representatives of affected tribal governments, a 
    summary of the nature of their concerns, and a statement supporting the 
    need to issue the regulation. In addition, Executive Order 13084 
    requires us to develop an effective process permitting elected 
    officials and other representatives of Indian tribal governments ``to 
    provide meaningful and timely input in the development of regulatory 
    policies on matters that significantly or uniquely affect their 
    communities.''
        Today's rule implements requirements specifically set forth by the 
    Congress in section 319 of the Act without the exercise of any 
    discretion by us. Accordingly, the requirements of section 3(b) of 
    Executive Order 13084 do not apply to this rule.
        This rule governs the reporting of air quality by States for MSAs 
    and, in some cases, areas that are significantly affected by transport 
    of pollutants from MSAs. In extensive public and intergovermental 
    coordination efforts during the development of the proposal, EPA 
    received no information which would suggest that the rule will impose 
    new requirements on Indian tribal governments nor will it significantly 
    or uniquely affect communities of Indian tribal governments. To the 
    extent that air pollution from upwind MSAs significantly affects any 
    lands within Indian country, this impact is not a result of, or 
    affected by, today's rule and would be addressed under existing 
    requirements governing the implementation of air quality standards.
    
    I. National Technology Transfer and Advancement Act
    
        Section 12(d) of the National Technology Transfer and Advancement 
    Act of 1995 (NTTAA), Public Law 104-113, section 12(d) (15 U.S.C. 272 
    note) directs EPA to use voluntary consensus standards in its 
    regulatory activities unless to do so would be inconsistent with 
    applicable law or otherwise impractical. Voluntary consensus standards 
    are technical standards (e.g., materials specifications, test methods, 
    sampling procedures, and business practices) that are developed or 
    adopted by voluntary consensus standards bodies. The NTTAA directs EPA 
    to provide Congress, through OMB, explanations when the Agency decides 
    not to use available and applicable voluntary consensus standards. This 
    action does not involve technical standards. Therefore, EPA did not 
    consider the use of any voluntary consensus standards.
    
    J. Congressional Review Act
    
        The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the 
    Small Business Regulatory Enforcement Fairness Act of 1996, generally 
    provides that before a rule may take effect, the agency promulgating 
    the rule must submit a rule report, which includes a copy of the rule, 
    to each House of the Congress and to the Comptroller General of the 
    United States. The EPA will submit a report containing this rule and 
    other required information to the U.S. Senate, the U.S. House of 
    Representatives, and the Comptroller General of the United States prior 
    to the publication of the rule in the Federal Register. This rule is 
    not a ``major rule'' as defined by 5 U.S.C. 804(2).
    
    IV. References
    
    CEQ, (1976) A Recommended Air Pollution Index, report prepared by 
    the Federal Interagency Task Force on Air Quality Indicators, 
    Council on Environmental Quality, Environmental Protection Agency, 
    and Department of Commerce.
    EPA, (1994) Measuring Air Quality: The Pollutant Standards Index, 
    U.S. Environmental Protection Agency, Office of Air Quality Planning 
    and Standards (MD-10), Research Triangle Park, NC, 27711, EPA 451/K-
    94-001.
    
    [[Page 42547]]
    
    EPA, (1999a) Guideline for Public Reporting of Daily Air Quality--
    Air Quality Index (AQI), U.S. Environmental Protection Agency, 
    Office of Air Quality Planning and Standards, Research Triangle 
    Park, NC, 27711, EPA-454/R-99-010.
    EPA, (1999b) Guideline for Developing an Ozone Forecasting Program, 
    U.S. Environmental Protection Agency, Office of Air Quality Planning 
    and Standards, Research Triangle Park, NC, 27711, EPA-454/R-99-009.
    EPA, (1999c) The Air Quality Index, U.S. Environmental Protection 
    Agency, Office of Air Quality Planning and Standards, Research 
    Triangle Park, NC, 27711, in preparation.
    Science Applications International Corporation, (1998) Report of 
    Eight Focus Groups on the Ozone Map, the Pollutant Standards Sub-
    index for Ozone, and the Ozone Health Effects Booklet, Science 
    Applications International Corporation, McLean, VA.
    U.S. Department of Commerce, (1998) Statistical Abstract of the 
    United States, U.S. Bureau of the Census.
    Whitfield, R.G.; Biller, W.F.; Jusko, M.J.; Keisler, JM (1996) A 
    probabilistic assessment of health risks associated with short-term 
    exposure to tropospheric ozone. Report prepared for U.S. EPA, OAQPS. 
    Argonne National Laboratory; Argonne, IL.
    Wolff, G.T., (1995) Letter from Chairman of the Clean Air Scientific 
    Advisory Committee to the EPA Administrator, dated November 30, 
    1995. EPA-SAB-CASAC-LTR-96-002.
    
    List of Subjects in 40 CFR Part 58
    
        Environmental protection, Air pollution control, Intergovernmental 
    relations, Reporting and recordkeeping requirements.
    
        Dated: July 23, 1999.
    Carol M. Browner,
    Administrator.
    
        Accordingly, 40 CFR part 58 is amended as follows:
    
    PART 58--AMBIENT AIR QUALITY SURVEILLANCE
    
        1. The authority citation for part 58 continues to read as follows:
    
        Authority: 42 U.S.C. 7410, 7601(a), 7613, and 7619.
    
        2. Section 58.50 is revised to read as follows:
    
    
    Sec. 58.50  Index reporting.
    
        (a) The State shall report to the general public through prominent 
    notice an air quality index in accordance with the requirements of 
    appendix G to this part.
        (b) Reporting is required by all Metropolitan Statistical Areas 
    with a population exceeding 350,000.
        (c) The population of a Metropolitan Statistical Area for purposes 
    of index reporting is the most recent decennial U.S. census population.
        3. Appendix G to part 58 is revised to read as follows:
    
    Appendix G to Part 58--Uniform Air Quality Index (AQI) and Daily 
    Reporting
    
    General Requirements
    
        1. What is the AQI?
        2. Why report the AQI?
        3. Must I report the AQI?
        4. What goes into my AQI report?
        5. Is my AQI report for my MSA only?
        6. How do I get my AQI report to the public?
        7. How often must I report the AQI?
        8. May I make exceptions to these reporting requirements?
    
    Calculation
    
        9. How does the AQI relate to air pollution levels?
        10. Where do I get the pollutant concentrations to calculate the 
    AQI?
        11. Do I have to forecast the AQI?
        12. How do I calculate the AQI?
    
    Background and Reference Materials
    
        13. What additional information should I know?
    
    General Requirements
    
    1. What Is the AQI?
    
        The AQI is a tool that simplifies reporting air quality to the 
    general public. The AQI incorporates into a single index 
    concentrations of 5 criteria pollutants: ozone (O3), 
    particulate matter (PM), carbon monoxide (CO), sulfur dioxide 
    (SO2), and nitrogen dioxide (NO2). The scale 
    of the index is divided into general categories that are associated 
    with health messages.
    
    2. Why Report the AQI?
    
        The AQI offers various advantages:
        a. It is simple to create and understand.
        b. It conveys the health implications of air quality.
        c. It promotes uniform use throughout the country.
    
    3. Must I Report the AQI?
    
        You must report the AQI daily if yours is a metropolitan 
    statistical area (MSA) with a population over 350,000.
    
    4. What Goes Into My AQI Report?
    
        i. Your AQI report must contain the following:
        a. The reporting area(s) (the MSA or subdivision of the MSA).
        b. The reporting period (the day for which the AQI is reported).
        c. The critical pollutant (the pollutant with the highest index 
    value).
        d. The AQI (the highest index value).
        e. The category descriptor and index value associated with the 
    AQI and, if you choose to report in a color format, the associated 
    color. Use only the following descriptors and colors for the six AQI 
    categories:
    
                            Table 1.--AQI Categories
    ------------------------------------------------------------------------
               For this AQI             Use this descriptor   And this color
    ----------------------------------------------------------------1-------
    0 to 50..........................  ``Good''............  Green.
    ------------------------------------------------------------------------
    51 to 100........................  ``Moderate''........  Yellow.
    ------------------------------------------------------------------------
    101 to 150.......................  ``Unhealthy for       Orange.
                                        Sensitive Groups''.
    ------------------------------------------------------------------------
    151 to 200.......................  ``Unhealthy''.......  Red.
    ------------------------------------------------------------------------
    201 to 300.......................  ``Very Unhealthy''..  Purple.
    ------------------------------------------------------------------------
    301 and above....................  ``Hazardous''.......  Maroon.\1\
    ------------------------------------------------------------------------
    1 Specific colors can be found in the most recent reporting guidance
      (Guideline for Public Reporting of Daily Air Quality--Air Quality
      Index (AQI)).
    
        f. The pollutant specific sensitive groups for any reported 
    index value greater than 100. Use the following sensitive groups for 
    each pollutant:
    
    ------------------------------------------------------------------------
     When this pollutant has an index value  Report these sensitive groups *
                above 100 * * *                            * *
    ------------------------------------------------------------------------
    Ozone..................................  Children and people with asthma
                                              are the groups most at risk.
    ------------------------------------------------------------------------
    PM2.5..................................  People with respiratory or
                                              heart disease, the elderly and
                                              children are the groups most
                                              at risk.
    ------------------------------------------------------------------------
    PM10...................................  People with respiratory disease
                                              are the group most at risk.
    ------------------------------------------------------------------------
    CO.....................................  People with heart disease are
                                              the group most at risk.
    ------------------------------------------------------------------------
    SO2....................................  People with asthma are the
                                              group most at risk.
    ------------------------------------------------------------------------
    
    [[Page 42548]]
    
    
    NO2....................................  Children and people with
                                              respiratory disease are the
                                              groups most at risk.
    ------------------------------------------------------------------------
    
        ii. When appropriate, your AQI report may also contain the 
    following:
        a. Appropriate health and cautionary statements.
        b. The name and index value for other pollutants, particularly 
    those with an index value greater than 100.
        c. The index values for sub-areas of your MSA.
        d. Causes for unusual AQI values.
        e. Actual pollutant concentrations.
    
    5. Is My AQI Report for My MSA Only?
    
        Generally, your AQI report applies to your MSA only. However, if 
    a significant air quality problem exists (AQI greater than 100) in 
    areas significantly impacted by your MSA but not in it (for example, 
    O3 concentrations are often highest downwind and outside 
    an urban area), you should identify these areas and report the AQI 
    for these areas as well.
    
    6. How Do I Get My AQI Report to the Public?
    
        You must furnish the daily report to the appropriate news media 
    (radio, television, and newspapers). You must make the daily report 
    publicly available at one or more places of public access, or by any 
    other means, including a recorded phone message, a public Internet 
    site, or facsimile transmission. When the AQI value is greater than 
    100, it is particularly critical that the reporting to the various 
    news media be as extensive as possible. At a minimum, it should 
    include notification to the media with the largest market coverages 
    for the area in question.
    
    7. How Often Must I Report the AQI?
    
        You must report the AQI at least 5 days per week. Exceptions to 
    this requirement are in section 8 of this appendix.
    
    8. May I Make Exceptions to These Reporting Requirements?
    
        i. If the index value for a particular pollutant remains below 
    50 for a season or year, then you may exclude the pollutant from 
    your calculation of the AQI in section 12.
        ii. If all index values remain below 50 for a year, then you may 
    report the AQI at your discretion. In subsequent years, if pollutant 
    levels rise to where the AQI would be above 50, then the AQI must be 
    reported as required in sections 3, 4, 6, and 7 of this appendix.
    
    Calculation
    
    9. How Does the AQI Relate to Air Pollution Levels?
    
        For each pollutant, the AQI transforms ambient concentrations to 
    a scale from 0 to 500. The AQI is keyed as appropriate to the 
    national ambient air quality standards (NAAQS) for each pollutant. 
    In most cases, the index value of 100 is associated with the 
    numerical level of the short-term standard (i.e., averaging time of 
    24-hours or less) for each pollutant. Different approaches are taken 
    for NO2, for which no short-term standard has been 
    established, and for PM2.5, for which the annual standard 
    is the principal vehicle for protecting against short-term 
    concentrations. The index value of 50 is associated with the 
    numerical level of the annual standard for a pollutant, if there is 
    one, at one-half the level of the short-term standard for the 
    pollutant, or at the level at which it is appropriate to begin to 
    provide guidance on cautionary language. Higher categories of the 
    index are based on increasingly serious health effects and 
    increasing proportions of the population that are likely to be 
    affected. The index is related to other air pollution concentrations 
    through linear interpolation based on these levels. The AQI is equal 
    to the highest of the numbers corresponding to each pollutant. For 
    the purposes of reporting the AQI, the sub-indexes for 
    PM10 and PM2.5 are to be considered 
    separately. The pollutant responsible for the highest index value 
    (the reported AQI) is called the ``critical'' pollutant.
    
    10. Where Do I Get the Pollutant Concentrations To Calculate the 
    AQI?
    
        You must use concentration data from population-oriented State/
    Local Air Monitoring Station (SLAMS) or parts of the SLAMS required 
    under 40 CFR 58.20 for each pollutant except PM. For PM, you need 
    only calculate and report the AQI on days for which you have 
    measured air quality data (e.g., particulate monitors often report 
    values only every sixth day). You may use particulate measurements 
    from monitors that are not reference or equivalent methods (for 
    example, continuous PM10 or PM2.5 monitors) if 
    you can relate these measurements by statistical linear regression 
    to reference or equivalent method measurements.
    
    11. Do I Have to Forecast the AQI?
    
        You should forecast the AQI to provide timely air quality 
    information to the public, but this is not required. If you choose 
    to forecast the AQI, then you may consider both long-term and short-
    term forecasts. You can forecast the AQI at least 24-hours in 
    advance using the most accurate and reasonable procedures 
    considering meteorology, topography, availability of data, and 
    forecasting expertise. The document ``Guideline for Developing an 
    Ozone Forecasting Program'' (the Forecasting Guidance) will help you 
    start a forecasting program. You can also issue short-term forecasts 
    by predicting 8-hour ozone values from 1-hour ozone values using 
    methods suggested in the Reporting Guidance, ``Guideline for Public 
    Reporting of Daily Air Quality.''
    
    12. How Do I Calculate the AQI?
    
        i. The AQI is the highest value calculated for each pollutant as 
    follows:
        a. Identify the highest concentration among all of the monitors 
    within each reporting area and truncate the pollutant concentration 
    to one more than the significant digits used to express the level of 
    the NAAQS for that pollutant. This is equivalent to the rounding 
    conventions used in the NAAQS.
        b. Using Table 2, find the two breakpoints that contain the 
    concentration.
        c. Using Equation 1, calculate the index.
        d. Round the index to the nearest integer.
    
                                                                Table 2.--Breakpoints for the AQI
    --------------------------------------------------------------------------------------------------------------------------------------------------------
                                                 These breakpoints                                                Equal these AQIs * *
    -----------------------------------------------------------------------------------------------------------------------*-----------
                                                                           PM10                                                               Category
             O3 (ppm)  8-hour          O3 (ppm)  1-   PM2.5  (g/    CO (ppm)     SO2 (ppm)     NO2 (ppm)      AQI
                                          hour 1          m>g/m3)           m3)
    --------------------------------------------------------------------------------------------------------------------------------------------------------
    0.000-0.064......................  ............   0.0-15.4            0-54       0.0-4.4      0.000-0.034       (2)       0-50      Good.
    0.065-0.084......................  ............  15.5-40.4          55-154       4.5-9.4      0.035-0.144       (2)       51-100    Moderate.
    0.085-0.104......................  0.125-0.164   40.5-65.4         155-254       9.5-12.4     0.145-0.224       (2)       101-150   Unhealthy for
                                                                                                                                         sensitive groups.
    0.105-0.124......................  0.165-0.204   4 65.5-150.4      255-354       12.5-15.4    0.225-0.304       (2)       151-200   Unhealthy.
    0.125-0.374......................  0.205-0.404   4 150.5-250.4     355-424       15.5-30.4    0.305-0.604    0.65-1.24    201-300   Very unhealthy.
    (3)..............................  0.405-0.504   4 250.5-350.4     425-504       30.5-40.4    0.605-0.804    1.25-1.64    301-400   ....................
    (3)..............................  0.505-0.604   4 350.5-500.4     505-604       40.5-50.4    0.805-1.004    1.65-2.04    401-500   Hazardous.
    --------------------------------------------------------------------------------------------------------------------------------------------------------
    1 Areas are generally required to report the AQI based on 8-hour ozone values. However, there are a small number of areas where an AQI based on 1-hour
      ozone values would be more precautionary. In these cases, in addition to calculating the 8-hour ozone index value, the 1-hour ozone index value may be
      calculated, and the maximum of the two values reported.
    
    [[Page 42549]]
    
    
    2 NO2 has no short-term NAAQS and can generate an AQI only above an AQI value of 200.
    3 8-hour O3 values do not define higher AQI values ( 301). AQI values of 301 or higher are calculated with 1-hour O3 concentrations.
    4 If a different SHL for PM2.5 is promulgated, these numbers will change accordingly.
    
        ii. If the concentration is equal to a breakpoint, then the 
    index is equal to the corresponding index value in Table 2. However, 
    Equation 1 can still be used. The results will be equal. If the 
    concentration is between two breakpoints, then calculate the index 
    of that pollutant with Equation 1. You must also note that in some 
    areas, the AQI based on 1-hour O3 will be more 
    precautionary than using 8-hour values (see footnote 1 to Table 2). 
    In these cases, you may use 1-hour values as well as 8-hour values 
    to calculate index values and then use the maximum index value as 
    the AQI for O3.
    [GRAPHIC] [TIFF OMITTED] TR04AU99.044
    
    Where:
    
    Ip = the index value for pollutantp
    Cp = the truncated concentration of          
    pollutantp
    BPHi = the breakpoint that is greater than or equal to 
    Cp
    BPLo = the breakpoint that is less than or equal to 
    Cp
    IHi = the AQI value corresponding to BPHi
    Ilo = the AQI value corresponding to BPLo.
    
        iii. If the concentration is larger than the highest breakpoint 
    in Table 2 then you may use the last two breakpoints in Table 2 when 
    you apply Equation 1.
    
    Example
    
        iv. Using Table 2 and Equation 1, calculate the index value for 
    each of the pollutants measured and select the one that produces the 
    highest index value for the AQI. For example, if you observe a 
    PM10 value of 210 g/m3, a 1-hour 
    O3 value of 0.156 ppm, and an 8-hour O3 value 
    of 0.130 ppm, then do this:
        a. Find the breakpoints for PM10 at 210 g/
    m3 as 155 g/m3 and 254 g/
    m3, corresponding to index values 101 and 150;
        b. Find the breakpoints for 1-hour O3 at 0.156 ppm as 
    0.125 ppm and 0.164 ppm, corresponding to index values 101 and 150;
        c. Find the breakpoints for 8-hour O3 at 0.130 ppm as 
    0.125 ppm and 0.374 ppm, corresponding to index values 201 and 300;
        d. Apply Equation 1 for 210 g/m3, 
    PM10:
    [GRAPHIC] [TIFF OMITTED] TR04AU99.045
    
        e. Apply Equation 1 for 0.156 ppm, 1-hour O3:
        [GRAPHIC] [TIFF OMITTED] TR04AU99.046
        
        f. Apply Equation 1 for 0.130 ppm, 8-hour O3:
        [GRAPHIC] [TIFF OMITTED] TR04AU99.047
        
        g. Find the maximum, 203. This is the AQI. The minimal AQI 
    report would read:
        v. Today, the AQI for my city is 203 which is very unhealthy, 
    due to ozone. Children and people with asthma are the groups most at 
    risk.
    
    Background and Reference Materials
    
    13. What Additional Information Should I Know?
    
        The EPA has developed a computer program to calculate the AQI 
    for you. The program works with Windows 95, it prompts for inputs, 
    and it displays all the pertinent information for the AQI (the index 
    value, color, category, sensitive group, health effects, and 
    cautionary language). The EPA has also prepared a brochure on the 
    AQI that explains the index in detail (The Air Quality Index), 
    Reporting Guidance (Guideline for Public Reporting of Daily Air 
    Quality) that provides associated health effects and cautionary 
    statements, and Forecasting Guidance (Guideline for Developing an 
    Ozone Forecasting Program) that explains the steps necessary to 
    start an air pollution forecasting program. You can download the 
    program and the guidance documents at www.epa.gov/airnow.
    
    [FR Doc. 99-19433 Filed 8-3-99; 8:45 am]
    BILLING CODE 6560-50-P
    
    
    

Document Information

Effective Date:
10/4/1999
Published:
08/04/1999
Department:
Environmental Protection Agency
Entry Type:
Rule
Action:
Final rule.
Document Number:
99-19433
Dates:
October 4, 1999.
Pages:
42530-42549 (20 pages)
Docket Numbers:
FRL-6409-7
RINs:
2060-AH92: Air Quality Index Reporting
RIN Links:
https://www.federalregister.gov/regulations/2060-AH92/air-quality-index-reporting
PDF File:
99-19433.pdf
CFR: (1)
40 CFR 58.50