ILLINOIS POLLUTION CONTROL BOARD
    June 5, 2003
     
    IN THE MATTER OF: )
     
      
      
      
      
      
      
    )
    NOISE RULE UPDATE: ) R03-8
    AMENDMENTS TO 35 ILL. ADM. ) (Rulemaking - Noise)
    CODE 900 AND 903 )
     
    Proposed Rule. Second Notice.
     
    OPINION AND ORDER OF THE BOARD (by M.E. Tristano and W.A. Marovitz):
     
    Pursuant to 35 Ill. Adm. Code Part 102 Subpart B and Sections 27 and 28 of the Illinois
    Environmental Protection Act (Act), 415 ILCS 5/27/28 (2002), the Illinois Pollution Control
    Board opened this rulemaking to amend and update the Board’s noise rules in Noise Rule
    Update: Amendments to 35 Ill. Adm. Code 900 and 903, R03-8 (Sept. 19, 2002).
     
    The noise rules affected are set forth at 35 Ill. Adm. Code 900 and 903. These are
    general provisions dealing with the definitions of acoustical terminology, prohibition against
    noise pollution, and sound measurement procedures. The proposed changes involve the updating
    of definitions and sound measurement procedures. The Board adopted these definitions and
    measurement procedures in 1973 in Noise Pollution Control Regulations, R72-2 (July 31, 1973),
    and modified them in 1987 in General Motors Corp. Proposed Amendments to 35 Ill. Adm. Code
    900.103 and 900.104, R83-7 (Jan. 22, 1987). In 1987, the Board modified the regulations by
    adding a one-hour equivalent sound averaging period based on General Motors Corporation’s
    proposal. The bases for the changes proposed in this rule are: extensive research conducted by
    the Board and the Department of Energy and Natural Resources
    1
    from 1986–1991 and the
    American National Standards Institute updates from the years 1998-2001.
     
    The Board also proposes to repeal Part 903, which specifies rules and regulations for the
    control of noise from motor racing facilities. Since the adoption of these rules, Section 25 of the
    Act has been modified to exclude organized sporting events, including motor racing facilities
    from the Board’s noise regulations. 415 ILCS 5/25 (2002).
     
    The instant rulemaking is closely associated with the recently opened docket Proposed
    New and Updated Rules for Measurement and Numerical Sound Emissions Standards
    Amendments to 35 Ill. Adm. Code 901 and 910, R03-9 (Feb. 20, 2003). R03-9 revises outdated
    numerical sound emission standards for property line noise sources found at 35 Ill. Adm. Code
    Parts 901 and adds Part 910 to the Board’s rules that incorporates noise measurement techniques
    currently contained only in Illinois Environmental Protection Agency (Agency) rules at 35 Ill.
    Adm. Code 951.
    1
    In 1995, the Department of Natural Resources Act P.A. 89-50 (eff. July 1, 1995) (20 ILCS
    5/801
    et seq
    . (2002))
     
    merged DENR into the Department of Natural Resources.
     

     
    2
     
    By today’s action the Board adopts the proposed rule for second notice, pursuant to the
    Illinois Administrative Procedure Act (5 ILCS 100/1-1). No comments were received during the
    additional public comment period of 45 days afforded this rule after the first notice period. The
    proposal adopted here is unchanged from that adopted by the Board’s April 3, 2003 proposed
    second-notice opinion and order. Noise Rule Update: Amendments to 35 Ill Adm. Code 900
    and 903, R03-8 (Apr. 3, 2003). The following opinion will provide a proposal overview,
    modifications made during the first notice period, and discuss the economic reasonableness and
    technical feasibility of the rule.
      
    PROCEDURAL HISTORY
     
    The Board issued a proposal for public comment on October 3, 2002. Noise Rule
    Update: Amendments to 35 Ill. Adm. Code 900 and 903, R03-8 (Oct. 3, 2002). The Board
    elicited comments from the public and those involved in prior rulemakings involving noise
    regulation. Individuals who were on the notice list were sent drafts of the rule and the hearing
    dates. In addition, the proposed rule was posted on the Board’s website. The Board has held
    three hearings in this matter. The first hearing was held in Chicago on November 7, 2002, and
    the second hearing was held in Springfield on November 21, 2002. There were no members of
    the public in attendance at the hearings. The Board received one comment from the Agency on
    December 12, 2002 (PC 1). On December 19, 2002, the Board adopted the proposal for first
    notice.
    2
    Finally, a hearing was conducted in Chicago on May 15, 2003 regarding the economic
    reasonableness and technical feasibility of the rule.
     
    The Board received seven public comments since the Board issued the proposal. The
    public comments are PC 1 and 5 filed by Kyle Rominger of the Agency; PC 2 filed by Paul
    Schomer of Schomer and Associates; PC 3 filed by Greg Zak of Noise Solutions; PC 4 filed by
    Thomas Thunder of Acoustic Associates, Ltd.; PC 6 filed by Joel Sternstein of the Attorney
    General’s Office for George Kamperman of Kamperman Associates Inc.; and PC 7 filed by Joel
    Sternstein of the Attorney General’s Office. The comments were generally supportive but did
    raise important issues which the Board will address later in this opinion.
     
    On April 3, 2003, the Board determined that due to the significant modifications made to
    the proposed rulemaking during first notice, a pre-second notice comment period of 45 days
    should be opened. All parties to the service list and commentors were given a copy of the
    Board’s revised proposal. The Board also published the modified rule on its website. The Board
    received no comments during the comment period.
     
    PROPOSAL OVERVIEW
     
    2
    Noise Rule Update: Amendments to 35 Ill. Adm. Code 900 and 903, R03-8 (Dec. 19, 2002).
    First notice publication occurred in the
    Illinois Register
    , February 7, 2003, at 1889
    et seq
    . and
    1909
    et seq
    .
     

     
    3
    The noise rules affected are set forth at 35 Ill. Adm. Code 900 and 903. These are
    general provisions dealing with the definitions of acoustical terminology, prohibition against
    noise pollution, and sound measurement procedures. The proposed changes involve the updating
    of definitions and sound measurement procedures. These definitions and measurement
    procedures were adopted in 1973 and were modified in 1987 in General Motors Corp. Proposed
    Amendments to 35 Ill. Adm. Code 900.103 and 900.104, R83-7 (Jan. 22, 1987). The most
    important updates relate to the definition of ambient, intermittent sound, and period of
    observation. The basis for these changes is the American National Standards Institute (ANSI)
    updates from the years 1998-2001. The Board also incorporates by reference the ANSI updates.
     
    The Board also proposes to repeal Part 903, which specifies rules and regulations for the
    control of noise from motor racing facilities. Since the adoption of these rules, Section 25 of the
    Environmental Protection Act has been modified to exclude organized sporting events, including
    motor racing facilities from the Board’s noise regulations. 415 ILCS 5/25 (2002).
     
      
    COMMENTS AND MODIFICATIONS
     
    During the first notice public comment period, the Board noted the need to include three
    additional definitions and the inclusion of another document by reference. These definitions are
    discrete tone, highly impulsive sound and the acronym for Land-Based Classification Standards.
     
    Discrete tone: a sound wave whose instantaneous sound pressure varies
    essentially as a simple sinusoidal function of time.
    3
     
     
    Highly impulsive sound either a single pressure peak or a single burst (multiple
    pressure peaks) for a duration usually less than one second. Examples of
    impulsive sound sources are a drop forge hammer and explosive blasting.
    4
     
     
    LBCS: the Land-Based Classification Standards which designate land use
    functions by means of numeric codes.
     
    Also, to be consistent with Noise Rule Update: Amendments to 35 Ill. Adm. Code 902,
    R03-9 (Feb. 20, 2003), the Board has incorporated by reference the
    International
    Electrotechnical Commission, IEC 804-2000, Integrating/Averaging Sound Level Meters
     
     
    During the first notice period, four of the public comments, PC 2, PC 4, PC 6, and PC 7,
    suggested that the Board incorporate the ANSI S12.9-1993 (R 1998)
    American National
    3
    This definition is taken from the Agency’s regulations at 35 Ill. Adm. Code 951.103.
     
    4
    Due to a typographical oversight, the first-notice opinion and order did not include a definition
    of impulsive sound. The Board has a current definition of impulsive sound found at 35 Ill. Adm.
    Code 900.103. Today, the Board includes a definition of “highly impulsive sound” to be
    consistent with the terminology used in the Board’s proposal in Noise Rule Update:
    Amendments to 35 Ill. Adm. Code 902, R03-9 (Feb. 20, 2003). The Board also includes
    erroneously omitted definitions for “bus,” “motor vehicle,” and “IHRA.”

     
    4
    Standard Quantities and Procedures for Description and Measurement of Environmental Sound,
    Part 3: Short-term Measurement with an Observer Present.
    Mr. Thunder’s comment is typical
    of those received. PC 4. Mr. Thunder notes that the Board has incorporated Part 1 which
    addressed definitions for standard quantities but does not include Part 3 which is the most
    relevant American National Standard dealing with the type of measurements and procedures. PC
    4 at 2. The Board agreed that it was logical to add Part 3 and modified the proposed rule to
    include this document as an incorporation by reference at Section 900.106.
     
    Mr. Thunder also suggested that the Board modify the definition of “background sound
    level” to be congruent to the definition in ANSI S12.9 Part 3. PC 4 at 2. Accordingly, the Board
    has changed the definition of “background sound level” to “background ambient sound level,”
    with a cross reference to 35 Ill. Adm. Code 910, which sets forth protocols for measuring the
    background ambient noise. Also, the Board added some clarifying language to the definition of
    “ambient” at Section 900.103. PC 2 at 2. Mr. Thunder argued that the use of the term “period
    of observation” within the draft is not fully consistent with current ANSI terminology and
    suggests that “measurement period” is more appropriate. PC 2 at 2. The Board agreed and made
    changes to Section 900.103 to reflect the new terminology.
     
    The Agency requested that the Board amend language to 35 Ill. Adm. Code 900.103 and
    900.104. PC 1 at 1. The reason for the requested changes was that the Agency no longer
    operates a noise program. PC 1 at 1. Therefore, the Agency requested that its affirmative
    obligations and discretionary authority under the Board’s noise regulations be repealed. The
    Board will continue to include discretionary authority in Section 900.103. The Board will not
    remove the affirmative obligations from Section 900.104. As Section 900.104 contained no
    changes at first notice, the Board is prohibited from making any changes for second notice.
    See
     
    5/ILCS 100/1-90(b)(1); 1 Ill. Adm. Code 229.600 (a)(3).
     
    MEASUREMENT PERIOD AND ONE HOUR EQUIVALENT SOUND LEVEL (LEQ)
    HISTORICAL PERSPECTIVE
     
    The Board adopted its first comprehensive noise regulation on July 31, 1973. Noise
    Pollution Control Regulations, R72-2 (July 31, 1973). In the Board’s opinion in support of the
    noise regulation, the Board describes the regulation as “designed to protect people in the state
    from the unreasonable exposure to environmental noise burdens.” Noise Pollution Control
    Regulations, R72-2 (July 31, 1973), slip op. at 20, 36. The limits established in 1973 and
    contained in Part 900 and 901 as adopted in 1973, calculated the nuisance noise level by taking
    the maximum sound pressure exerted during the observation period. Noise Pollution Control
    Regulations, R72-2 (July 31, 1973), slip op. at 6. Further, the regulations allowed one to define
    the period of measurement as 24 hours.
     
    General Motors Corporation (GM) filed a petition for modification of the Board’s noise
    regulation on February 24, 1983. GM proposed amendments to 35 Ill. Adm. Code 900.103(b)
    “Measurement Procedures” applicable to Part 901 to require the use of “one-hour Leq averaging
    in determining compliance with the regulation.” The Board held hearings on the proposal on
    June 22 and November 22-23, 1983. General Motors Corp. Proposed Amendments to 35 Ill.
    Adm. Code 900.103 and 900.104, R83-7 (Jan. 22, 1987), slip op. at 1. GM, the Agency and

     
    5
    Department of Natural Resources were the only active participants in these proceedings. On
    November 7, 1985, the Board proposed for first notice these amendments to its rules.
    Subsequent to publication the Board received three public comments which led to modification
    of the proposed rule but not the areas addressing Leq or the measurement period. General Motors
    Corp. Proposed Amendments to 35 Ill. Adm. Code 900.103 and 900.104, R83-7
    (Jan. 22, 1987), slip op. at 2.
     
    By amending Section 900.103(b) in 1987, the Board further endorsed the use of ANSI
    standards and introduced Leq averaging as the statistical measure for measuring noise and
    established a one-hour measurement period. The Board’s decision of 1987 reflected the
    recognition of enhanced measuring capabilities and the emergence of Leq as the standard sound
    level measurement. GM was concerned that the longer 24-hour period, prior to Board
    modification, coupled with an inaccurate equation for determining equivalent sound levels,
    would overstate fluctuating sound of high intensity. In support of adoption of the Leq, the Board
    referred to research completed contemporaneous or subsequent to the 1973 rule adoption such
    as:
     
    1)
    Public Health and Welfare Criteria for Noise
    , published July 27, 1973 by the
    United States Environmental Protection Agency (USEPA);
     
    2)
    Information on Levels of Environmental Noise Requisite to Protect Public Health
    and Welfare with an Adequate Margin of Safety
    , published in April 1974 by the
    USEPA;
     
    3)
    Toward a National Strategy for Noise Control
    , published in April 1977 by the
    USEPA’s former Office of Noise Abatement and Control;
     
    4)
    Sound Level Descriptors for Determination of Compatible Land Use
    , from ANSI
    S3.23-1980; and
     
    5)
    Method for Assessment of High-Energy Impulsive Sounds with Respect to
    Residential Communities
    , from ANSI S12.4-198X (June 1983 Draft).
    5
     
     
    Each of these documents provided support that Leq averaging was clearly becoming the standard
    sound level measure to accurately describe community response to noise. General Motors Corp.
    Proposed Amendments to 35 Ill. Adm. Code 900.103 and 900.104, R83-7 (Jan. 22, 1987), slip
    op. at 11. Once the Board accepted the concept that use of a measurement statistic which
    averages sound pressure levels as appropriate rather than the maximum sound pressure, the
    Board needed to address the period of measurement. In 1987, much of the literature spoke about
    a 24-hour observation period, but the Board concluded that if an averaging method such as Leq
    were used, then requiring a 24-hour observation for each of the 8 octave bands would be too
    daunting a requirement. General Motors Corp. Proposed Amendments to 35 Ill. Adm. Code
    5
    General Motors Corp. Proposed Amendments to 35 Ill. Adm. Code 900.103 and 900.104, R83-
    7 (Jan. 22, 1987), slip op. at 10-11.

     
    6
    900.103 and 900.104, R83-7 (Nov. 7, 1985), (Jan. 22, 1987). The Board determined that an
    observation period of one hour would be a reasonable requirement for enforcement purposes.
     
    During first notice the Board circulated Part 900 without modifying either the use of Leq
    or the one-hour period of observation for all types of sound measurement. Seven public
    comments were received suggesting that the Board further enhance its rule to reflect the
    dichotomy between steady and non-steady sound. The commenters agree that a one-hour
    measurement period is reasonable when confronted with non-steady sound but excessively
    lengthy when the potential noise pollution is caused by a steady source. Some suggest a
    modification of the observation period for steady sound in the range of one minute (PC 3, PC 4),
    10 minutes (PC 2), and 30 minutes (PC 4). The Board modified the first notice proposal to
    reflect a ten-minute measurement period for steady sound; no comments were received from the
    public during the pre-second notice period. In today’s proposal at Section 900.103(b)(1)(B), the
    Board proposes at least a ten-minute measurement period for steady sound.
     
    The Board agrees to modify the first-notice proposal to reflect a difference in the period
    of observation for steady and non-steady sound emissions. It accepts the argument that the Leq
    measurement of steady sound would not be significantly affected by reducing the measurement
    period.
     
    In addition, the Board received technical and non-substantive comments from the Joint
    Committee on Administrative Rules which the Board incorporates into the second-notice
    proposal.
     
    ECONOMIC REASONALBENESS AND TECHNICAL FEASIBLILITY OF THE
    PROPOSAL
     
    During the first notice, the Board has received no comments discussing economic
    reasonableness and technical feasibility of the proposed rule. On April 9, 2003, pursuant to
    Section 27(b) of the Act (415 ILCS 5/27(b) (2002)), the Board requested that the Department of
    Commerce and Economic Opportunity (DCEO) conduct an economic impact study on the
    proposed rule. On April 17, 2003, DCEO responded that does not have staff or budget resources
    to perform economic impact studies on proposed rulemaking. At the May 15, 2003 hearing on
    the economic reasonableness and technical feasibility of the proposed rule, the Board provided
    copies of the DCEO letter and the Boards’ request. The Board received no comments at hearing
    or public notice.
     
    CONCLUSION
     
    The Board today proposes for second notice amendments to the Board’s noise rules. The
    Board is adopting the proposed rule with no change from its proposed second notice.
     

     
    7
    ORDER
     
    The Board directs that the following rule be filed with the Joint Committee on
    Administrative Rules for second-notice review.
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE H: NOISE
    CHAPTER I: POLLUTION CONTROL BOARD
     
    PART 900
    GENERAL PROVISIONS
     
    Section
    900.101 Definitions
    900.102 Prohibition of Noise Pollution
    900.103 Measurement Procedures
    900.104 Burden of Persuasion Regarding Exceptions
    900.105
    900.106
    Severability
    Incorporation by Reference
     
      
    APPENDIX A Old Rule Numbers Referenced OLD RULE NUMBERS
    REFERENCED
     
    AUTHORITY: Implementing Section 25 and authorized by Section 27 of the Environmental
    Protection Act (Ill. Rev. Stat. 1985, ch. 111 1/2, pars. 1025 and 1027) [415 ILCS 5/25 and 27].
     
    SOURCE: Originally filed as Part 1 of Chapter 8: Noise Pollution, effective August 10, 1973;
    amended at 2 Ill. Reg. 27, p. 223, effective June 26, 1978; amended at 5 Ill. Reg. 6371,
    effective June 1, 1981; amended at 5 Ill. Reg. 8533, effective August 10, 1981; amended at 6
    Ill. Reg. 10960, effective September 1, 1982; codified at 7 Ill. Reg. 13579; amended in R83-7
    at 11 Ill. Reg. 3121, effective January 28, 1987; amended in R03-8 at ____ Ill. Reg. ___,
    effective ________.
     
    Section 900.101 Definitions
     
    Except as hereinafter stated and unless a different meaning of a term is clear from its context, the
    definitions of terms used in this Chapter are shall be the same as those used in the Environmental
    Protection Act. All definitions of acoustical terminology must shall be in conformance with
    those contained in American National Standards Institute (ANSI) S1.1 – 1994 1960 (R1999)
    “American National Standard Acoustical Terminology”and S12.9- 1988 (R1998) “American
    National Standard Quantities and Procedures for Description and Measurement of Environmental
    Sound - Part 1,” incorporated by reference at Section 900.106. As used in 35 Ill. Adm. Code
    900 through 910 905, the following terms mean:
     
    A-Weighted Sound Level: dB(A), in decibels, a frequency weighted ten times the
    logarithm to the base 10 of the square of the ratio of the A-weighted (and time-averaged)

     
    8
    sound pressure level, to the reference sound pressure of 20 micropascal. The frequency
    and time weighting must be determined by the use of the metering characteristics and A-
    weighted network specified in accordance with ANSI §1.4-1971 (R. 1976) S1.4–1983
    (R2001) “American National Standard Specification for Sound Level Meters,”
    incorporated by reference at Section 900.106 and the latest revisions thereof. The unit of
    sound level is the decibel (dB) with the letter (A) appended to the decibel unit symbol to
    indicate the frequency weighting and written as dB(A).
     
    AHRA: American Hot Rod Association or its successor body.
     
    Ambient: the all-encompassing sound associated with a given environment without
    contributions from the noise source or sources of interest.
     
     
    Angle of incidence: the orientation of the microphone relative to the sound source.
     
    ANSI: American National Standards Institute or its successor bodies.
     
    Antique vehicle: a motor vehicle that is more than 25 years of age or a bona fide replica
    thereof and which is driven on the highways only going to and returning from an antique
    auto show or an exhibition, or for servicing or demonstration, or a fire-fighting vehicle
    more than 20 years old which is not used as fire-fighting equipment but is used only for
    the purpose of exhibition or demonstration.
     
    Background ambient Sound Level: means the ambient sound level the A-weighted sound
    level, measured in accordance with the procedures specified in 35 Ill. Adm. Code 910.
    Section 900.103, which is exceeded 90 percent of the time during the period of
    observation, during which sounds from motor racing facilities are inaudible. The period
    of observation need not necessarily be contiguous; however, the period of observation
    must be at least of 10 minutes duration.
     
     
    Bus: every motor vehicle designed for carrying more than 10 passengers and used for the
    transportation of passengers; and every motor vehicle, other than a taxicab, designed and
    used for the transportation of persons for compensation.
     
    C-weighted Sound Level: in decibels, a frequency-weighted sound pressure level,
    determined by the use of the metering characteristics and C-weighted network specified
    in ANSI document §1.4-1971 S1.4-1983 (R2001. 1976) “ American National Standard
    Specification for Sound Level Meters.,” incorporated by reference at Section 900.106.
     
    Construction: on-site erection, fabrication, installation, alteration, demolition or removal
    of any structure, facility, or addition thereto, including all related activities including, but
    not restricted to, clearing of land, earth-moving, blasting and landscaping.
     
    Daytime hours: 7:00 am to 10:00 pm, local time.
     
    dB(A): see “A-weighted Sound Level.”

     
    9
     
    Dealer: every person engaged in the business of selling vehicles to persons who purchase
    such vehicles for purposes other than resale, and who has an established place of business
    for such activity in this state.
     
    Decibel (dB): a unit of measure, on a logarithmic scale to the base 10, of the ratio of the
    magnitude of a particular sound pressure to a standard reference pressure, which, for
    purposes of this Chapter, shall be 20 micronewtons per square meter (μuN/m
    2
    ) or 20
    micropascals (u
    µ
    Pa).
     
    Discrete tone: a sound wave whose instantaneous sound pressure varies essentially as a
    simple sinusoidal function of time.
     
    Drag racing: any acceleration contest between two racing vehicles racing from a
    standing start over a precisely measured, straight line course.
     
    Drag racing facility: any motor racing facility upon which is conducted drag racing.
     
    Drag racing vehicle: any racing vehicle which is participating in a drag race at a drag
    racing facility.
     
    Exhaust system: the system comprised of a combination of components which provides
    for the enclosed flow of exhaust gas from engine parts to the atmosphere.
     
    Existing motor racing facility: any motor racing facility, the construction of which
    commenced prior to August 10, 1973.
     
    Existing property-line-noise-source: any property-line-noise-source, the construction or
    establishment of which commenced prior to August 10, 1973. For the purposes of this
    sub-section, any property-line-noise-source whose A, B or C land use classification
    changes, on or after August 10, 1973, is shall not be considered an existing property-line-
    noise-source.
     
    Farm tractor: every motor vehicle designed and used primarily as a farm implement for
    drawing wagons, plows, mowing machines and other implements of husbandry, and
    every implement of husbandry which is self-propelled.
     
    Fast Dynamic Characteristic: the dynamic characteristic specified as fast in ANSI §S1.4-
    198371 (R-2001. 1976) “American National Standard Specification for Sound Level
    Meters,” incorporated by reference at Section 900.106 and the latest revision thereof.
     
    Fast meter response: as specified in ANSI §1.4-1971, S1.4–1983 (R2001) “American
    National Standard Specification for Sound Level Meters,” incorporated by reference at
    Section 900.106 or subsequent revisions.
     

     
    10
    Fluctuating sound: a class of non-steady sound where sound pressure level varies over a
    range greater than 6 decibels (dB) with the “slow” meter characteristic, and where the
    meter indication does not equal the ambient level more than once during the
    measurement period of observation.
     
     
    Frequency-weighted sound pressure: root mean square of the instantaneous sound
    pressure which is frequency-weighted (i.e., filtered) with a standard frequency
    characteristic (e.g., A or C) and exponentially time-weighted in accordance with the
    standardized characteristics slow (S), fast (F), impulse (I) or peak, with both weightings
    specified in accordance with ANSI S1.4–1983 (R2001) “American National Standard
    Specification for Sound Level Meters,” incorporated by reference at Section 900.106.
    The frequency weighting used shall be specified explicitly (e.g., A, C or octave band).
    The unit frequency-weighted sound pressure is the pascal (Pa).
     
    Gross Vehicle Weight (GVW): the maximum loaded weight for which a motor vehicle is
    registered or, for vehicles not so registered, the value specified by the manufacturer as the
    loaded weight of the vehicle.
     
    Highly Impulsive Sound: either a single pressure peak or a single burst (multiple pressure
    peaks) for a duration usually less than one second. Examples of highly impulsive sound
    sources are drop forge hammer and explosive blasting.
     
    Highway: the entire width between the boundary lines of every way publicly maintained
    when any part thereof is open to the use of the public for purposes of vehicular travel.
     
    Impulsive sound: either a single pressure peak or a single burst (multiple pressure peaks)
    for a duration usually less than one second. Examples of impulsive sound sources are a
    drop forge hammer and explosive blasting.
     
    IHRA: International Hot Rod Association or its successor body.
     
    Intermittent sound: a class of nonsteady sound where the meter indicates a sound
    pressure level equal to the ambient level two or more times during the measurement
    period of observation. The period of time during which the level of the sound remains at
    a value different from that of the ambient is of the order of one second or more.
     
    LBCS: the Land-Based Classification Standards which designate land use functions by
    means of numeric codes.
     
    Leqeq: equivalent continuous sound pressure level in decibels: ten times the logarithm to
    the base ten of the ratio of a time mean square sound pressure, during the specified time
    period, to the square of reference sound pressure. The reference sound pressure is 20
    micronewtons per square meter or equivalent continuous frequency-weighted sound
    pressure.
     
     
    Leq (A): A-weighted time-average (equivalent-continuous) sound pressure level.

     
    11
     
    Leq (octave band-Hz): time-average (equivalent-continuous) sound pressure level in the
    octave band specified by its center frequency e.g. Leq (125-Hz).
     
    Measurement Period of observation: the time interval during which acoustical data are
    obtained. The measurement period of observation is determined by the characteristics of
    the noise being measured and must be at least ten times as long as the response time of
    the instrumentation. The greater the variation in indicated sound level, the longer the
    observation time must be for a given expected precision of the measurement.
     
    Midget racing vehicle: a front engine, single seat, openwheel racing car smaller and of
    lesser engine displacement then standard cars of the type.
     
    Motor racing facility: any facility or course upon which is conducted motor racing
    activities or events.
     
    Motor driven cycle: every motorcycle, motor scooter, or bicycle with motor attached,
    with less than 150 cubic centimeter piston displacement.
     
    Motor vehicle: every vehicle which is self-propelled and any combination of vehicles
    which are propelled or drawn by a vehicle which is self-propelled.
     
    Motorcycle: every motor vehicle having a seat or saddle for the use of the rider and
    designed to travel on not more than 3 wheels in contact with the ground, but excluding a
    tractor.
     
     
    Motorcycle racing: any racing event between two or more motorcycles.
     
    Motorcycle racing facility: any motor racing facility upon which is conducted
    motorcycle racing, except oval racing facilities or drag racing facilities.
     
    Muffler: a device for abating the sounds of escaping gases of an internal combustion
    engine.
     
    NHRA: National Hot Rod Association or its successor body.
     
    New motor racing facility: any motor racing facility, the construction of which
    commenced on or after August 10, 1973.
     
    New snowmobile: a snowmobile, the equitable or legal title to which has never passed to
    a person who purchases it for purposes other than resale.
     
    Nighttime hours: 10:00 pm to 7:00 am, local time.
     
    Noise floor: the electrical noise (in decibels) of the sound measurement system. When
    the noise floor is determined by placing a calibrator over the microphone of the sound

     
    12
    measurement system, the noise floor may include acoustic noise due to leakage around
    the calibrator.
     
    Noise pollution: the emission of sound that unreasonably interferes with the enjoyment
    of life or with any lawful business or activity.
     
    Non-steady sound: a sound whose sound pressure level shifts significantly during the
    measurement period of observation. Meter variations are greater than +/- 3 dB using the
    “slow” meter characteristic.
     
    Octave band sound pressure level: the sound pressure level for the sound being measured
    contained within the specified octave band. The reference pressure is 20 micronewtons
    per square meter.
     
    Oval racing: any contest between two or more racing vehicles on a closed or oval racing
    surface.
     
    Oval racing facility: any motor racing facility, upon which is conducted oval racing.
     
    Oval racing vehicle: any racing vehicle which is participating in an oval race at an oval
    racing facility.
     
    Pascal (Pa): a unit of pressure. One pascal is equal to one newton per square meter.
     
    Passenger car: a motor vehicle designed for the carrying of not more than ten persons,
    including a multi-purpose passenger vehicle, except any motor vehicle of the second
    division as defined in 625 ILCS 5/1-146 Ill. Rev. Stat. 1981, ch. 95-1/2, par. 1-146, and
    except any motorcycle or motor driven cycle. t+1
     
    Person: any individual, corporation, partnership, firm, association, trust, estate, public or
    private institution, group, agency, political subdivision of this State, any other State or
    political subdivision or agency thereof or any legal successor, representative, agent or
    agency of the foregoing.
     
    Preferred frequencies: those frequencies in Hertz preferred for acoustical measurements
    which, for the purposes of this Chapter, consist of the following set of values: 20, 25,
    31.5, 40, 50, 63, 80, 100, 125, 160, 200, 250, 315, 400, 500, 630, 800, 1000, 1250, 1600,
    2000, 2500, 3150, 4000, 5000, 6300, 8000, 10,000, 12,500.
     
    Prominent discrete tone: sound, having a one-third octave band sound pressure level
    which, when measured in a one-third octave band at the preferred frequencies, exceeds
    the arithmetic average of the sound pressure levels of the two adjacent one-third octave
    bands on either side of such one-third octave band by:
     

     
    13
    5 dB for such one-third octave band with a center frequency from 500 Hertz to
    10,000 Hertz, inclusive. Provided: such one-third octave band sound pressure
    level exceeds the sound pressure level of each adjacent one-third octave band, or;
     
    8 dB for such one-third octave band with a center frequency from 160 Hertz to
    400 Hertz, inclusive. Provided: such one-third octave band sound pressure level
    exceeds the sound pressure level of each adjacent one-third octave band, or;
     
    15 dB for such one-third octave band with a center frequency from 25 Hertz to
    125 Hertz, inclusive. Provided: such one-third octave band sound pressure level
    exceeds the sound pressure level of each adjacent one-third octave band.
     
    Property-line-noise-source: any equipment or facility, or combination thereof, which
    operates within any land used as specified by 35 Ill. Adm. Code 901.101. Such
    equipment or facility, or combination thereof, must be capable of emitting sound beyond
    the property line of the land on which operated.
     
    Quasi-steady sound: a train of two or more acoustical impulses. Examples of quasi-
    steady sound are that from riveting and pneumatic hammer.
     
    Racing vehicle: every self-propelled device, in, upon or by which any person may be
    transported and which is participating in a motor racing activity or event at a motor
    racing facility.
     
    Reflective surface: any building, hillside, or similar object (other than the flat ground
    surface) that reflects sufficient sound to affect the sound pressure level readings obtained
    from a noise source. Not included as reflective surfaces are small objects such as trees,
    posts, chain-linked fences, fire hydrants, vegetation such as bushes and shrubs, or any
    similar object.
     
    Registered: a vehicle is registered when a current registration certificate or certificates
    and registration plates have been issued for it under the laws of any state pertaining to the
    registration of vehicles.
     
    Residential dwelling unit: all land used as specified by the Land-Based Classification
    Standards (LBCS) Standard Land Use Coding Manual (SLUCM) Codes 1100 through
    1340 190 and those portions of land used as specified by LBCS SLUCM Code 6222 6741
    used for sleeping.
     
     
    SAE: Society of Automotive Engineers.
     
    Slow Dynamic Characteristic: the dynamic characteristic specified as "Slow" in ANSI
    document §1.4-1971 (R. 1976) S1.4–1983 (R2001) " American National Standard
    Specification for Sound Level Meters.,” incorporated by reference at Section 900.106.
     

     
    14
    SLUCM: the Standard Land Use Coding Manual (1969, United States Government
    Printing Office) which designates land activities by means of numerical codes.
      
     
    Snowmobile: a self-propelled device designed for travel on snow or ice or natural terrain
    steered by skis or runners, and supported in part by skis, belts, or cleats.
     
    Sound: a physical disturbance causing an oscillation in pressure in a medium (e.g., air)
    that is capable of being detected by the human ear or a sound measuring instrument.
     
    Sound exposure (SE): time integral of squared, frequency-weighted instantaneous sound
    pressure over a given time interval. The time period of integration must be specified:
    when the sound exposure of the background noise is a significant contributor to the total
    sound exposure; or when the threshold sound level of the instrument (a level below which
    the instrument does not accumulate contributions to the integral) used is above the level
    of the background noise; or when such data is needed to identify a source; or when the
    time period of integration is otherwise useful. The customary unit for sound exposure is
    pascal-squared second (Pa
    2
    -s).
     
    Sound exposure level (SEL or LeT): ten (10) times the logarithm to the base 10 of the
    ratio of sound exposure to the reference sound exposure (Eo) of 400 micropascal-squared
    seconds (μPa
    2
    -s). For a given measurement time period of T seconds, the sound
    exposure level (LeT ) is related to the time-average sound level (LpT) as follows: LeT =
    LpT+ log (T/to) where to is the reference duration of 1 second. The time period of
    intergration (T) must be specified. The frequency weighting used must be specified
    explicitly (e.g., A, C or octave band). The A-weighted SEL and C-weighted SEL are
    abbreviated ASEL and CSEL respectively. An octave band SEL is expressed in terms of
    the center frequency (e.g., SEL at 125-Hz). The unit for sound exposure level is decibel
    (dB).
     
    Sound level (weighted sound pressure level): in decibels, a weighted sound pressure
    level, determined by the use of metering characteristics and frequency weightings
    specified in ANSI §1.4-1971 "Specification for Sound Level Meters." 20 times the
    logarithm to the base 10 of the ratio of the frequency-weighted (and time-averaged)
    sound pressure to the reference pressure of 20 micropascals. The frequency weighting
    used shall be specified explicitly (e.g., A, C or octave band). The unit for sound level is
    decibel (dB).
     
    Sound pressure: the root mean square of the instantaneous sound pressures during a
    specified time interval in a stated frequency band. The unit for sound pressure is pascal
    (Pa).
     
    Sound pressure level: in decibels, 20 times the logarithm to the base 10 of the ratio of the
    magnitude of a particular sound pressure to the standard reference sound pressure of 20
    micropascals. The standard reference pressure is 20 micronewtons per square meter.
    ANSI S12.9- 1988 (R1998) “American National Standard Quantities and Procedures for
    Description and Measurement of Environmental Sound - Part 1,” incorporated by

     
    15
    reference at Section 900.106, reserves the term sound pressure level to denote the
    unweighted sound pressure. The unit for sound pressure level is decibel (dB).
     
    Special mobile equipment: every vehicle not designed or used primarily for the
    transportation of persons or property and only incidentally operated or moved over a
    highway, including but not limited to: ditch digging apparatus, well-boring apparatus and
    road construction and maintenance machinery such as asphalt spreaders, bituminous
    mixers, bucket loaders, tractors other than truck tractors, leveling levelling graders,
    finishing machines, motor graders, road rollers, scarifiers, earth-moving carryalls and
    scrapers, power shovels and drag lines, and self-propelled cranes and other earth-moving
    equipment.
     
    Special-motor-racing-event: any motor racing event held on two consecutive days or less
    in which a substantial number of out-of-state motor racing vehicles are competing and
    which has been designated as such a special-motor-racing-event by the owner or operator
    of the motor racing facility.
     
    Sports car: any automobile which meets the requirements and specifications of the
    General Competition Rules of the Sports Car Club of America, or its successor body, or
    any other sports car organization.
     
    Sports car racing: any competitive event involving one or more sports cars.
     
    Sports car racing facility: any motor racing facility upon which is conducted sports car
    racing.
     
    Sports car racing vehicles: any racing vehicle which is participating in a sports car race
    at a sports car racing facility.
     
    Sprint racing vehicle: a front-engined open wheel racing car used especially on short dirt
    tracks.
     
    Supercharged racing vehicle: a racing vehicle equipped with a blower or compressor for
    increasing the volume air charge of an internal combustion engine over that which would
    be drawn in through the pumping action of the pistons.
     
    Steady sound: a sound whose sound pressure level remains essentially constant (that is,
    meter fluctuations are negligibly small) during the measurement period of observation.
    Meter variations are less than or equal to +/- 3 dB using the “slow” meter characteristic.
     
    Tactical military vehicle: every vehicle operated by any federal or state military
    organization and designed for use in field operations, but not including vehicles such as
    staff cars and personnel carriers designed primarily for normal highway use.
     
    Time-average sound level (or equivalent-continuous sound level or equivalent-continuous
    frequency-weighted sound pressure level): 20 times the logarithm to the base 10 of the

     
    16
    ratio of the time-average (frequency-weighted) sound pressure to the reference pressure
    of 20 micropascal. The frequency weighting used must be specified explicitly (e.g., A, C
    or octave band). The unit of time-average sound level is the decibel (dB).
     
    Time-average (frequency-weighted) sound pressure: square root of the quotient of the
    time integral of frequency-weighted squared instantaneous sound pressures divided by
    the time period of integration; or the square root of the quotient of the sound exposure, in
    pascal-squared seconds (Pa
    2
    –s), in a specified time period, divided by the time period of
    integration in seconds. The frequency weighting used must be specified explicitly (e.g.,
    A, C or octave band). The unit of time-average sound pressure is the pascal (Pa).
     
    Unregulated safety relief valve: a safety relief valve used and designed to be actuated by
    high pressure in the pipe or vessel to which it is connected and which is used and
    designed to prevent explosion or other hazardous reaction from pressure buildup, rather
    than being used and designed as a process pressure blowdown.
     
    Used motor vehicle: a motor vehicle that is not a new motor vehicle.
     
    Vehicle: every device in, upon, or by which any person or property is or may be
    transported or drawn upon a highway.
     
    Weekday: any day which occurs during the period of time commencing at 10:00 p.m.
    Sunday and ending at 10:00 p.m. Friday during any particular week.
     
    Weekend day: any day which occurs during the period of time commencing at 10:00
    p.m. Friday and ending at 10:00 p.m. Sunday during any particular week.
     
    Well-maintained muffler: any muffler which is free from defects which affect its sound
    reduction. Such muffler shall be free of visible defects such as holes and other acoustical
    leaks.
     
    (Source: Amended at ___. Reg. ____, effective ________)
     
    Section 900.103 Measurement Procedures
     
    a) Procedures Applicable to all of 35 Ill. Adm. Code: Subtitle H, Chapter I
     
    The Agency may adopt procedures which set forth criteria for the measurement of
    sound for all Parts except 35 Ill. Adm. Code 900 and 901. Such procedures shall
    be in substantial conformity with standards and recommended practices
    established by the American National Standards Institute, Inc. (ANSI) or the
    Society of Automotive Engineers, Inc. (SAE), incorporated by reference at
    Section 900.106. and the latest revisions thereof, including ANSI S1.1-1960,
    ANSI §1.8-1969, ANSI §1.2-1962, and SAE J-184. Such procedures shall be
    revised from time to time to reflect current engineering judgment and advances in
    noise measurement techniques. Such procedures, and revisions, thereof, shall not

     
    17
    become effective until filed with the Administrative Code Division of the Office
    of the Secretary of State as required by the Illinois Administrative Procedure Act
    Ill. Rev. Stat. 1985, ch. 127, par. 1001 et. seq. Measurement Procedures for
    35 Ill. Adm. Code 900 and 901 shall conform to 35 Ill. Adm. Code 910.
     
    b) Procedures Applicable only to 35 Ill. Adm. Code 901
     
    1) All measurement and all measurement procedures to determine whether
    emissions of sound comply with 35 Ill. Adm. Code 901 shall be in
    substantial conformity with ANSI §1.6-1967, ANSI §1.4-1971 -- Type I
    Precision, ANSI §1.11-1966, and ANSI §1.13-1971 Field Method, and
    shall with the exception of measurements to determine whether emissions
    of sound comply with 35 Ill. Adm. Code 901.109, be based on Leqeq
    averaging, as defined in 35 Ill. Adm. Code 900.101, using a reference time
    as follows: of one hour.
     
    A) Except as specified in subsection (b)(1)(B) for steady sound,
    below, a reference time of at least 1 hour shall be used for all
    sound measurements and measurement procedures.
     
    B) For measurement of steady sound as defined in section 900.101,
    the reference time shall be at least 10 minutes.
     
    2)
    All such measurements and measurements procedures under subsection
    (b)(1), above, for the 1-hr Leq must correct, or provide for the correction
    of such emissions, for the presence of ambient or background noise as
    defined in ANSI §1.13-1971 in accordance with the procedures in 35 Ill.
    Adm. Code 910. All measurements must be in conformity with the
    following ANSI standards, incorporated by reference at Section 900.106:
     
    A) ANSI S1.4-1983 (R2001) “American National Standard
    Specification for Sound Level Meters.”
     
    B) ANSI S1.6-1984 (R2001) “American National Standard Preferred
    Frequencies, Frequency Levels, and Band Numbers for Acoustical
    Measurements.”
     
    C) ANSI S1.11-1986 (R1998) “American National Standard
    Specification for Octave-Band and Fractional-Octave-Band
    Analog and Digital Filters.”
     
    D) ANSI S1.13-1995 (R1999) “American National Standard
    Measurement of Sound Pressure Level in Air.”
     
    E) ANSI S12.9-1993 (R1998) “American National Standard
    Quantities and Procedures for Description and Measurement of

     
    18
    Environmental Sound - Part 3: Short-Term Measurements With an
    Observer Present.”
     
    c) Procedures Applicable only to 35 Ill. Adm. Code 902
     
    1) Measurement procedures to determine whether emissions of sound comply
    with 35 Ill. Adm. Code 902.120 through 902.123 must shall be in
    substantial conformity with the following ANSI standards incorporated by
    reference at Section 900.106: ANSI §1.4-1971 -- Type I Precision or Type
    II General Purpose, and ANSI §1.13-1971 Field Method, provided that
     
    A) ANSI S1.4-1983 (R2001) “American National Standard
    Specification for Sound Level Meters.”
     
    B) ANSI S1.13-1995 (R1999) “American National Standard
    Measurement of Sound Pressure Level in Air.”
     
    2) The
    procedures for sound measurement under 35 Ill. Adm. Code 902.123
    must conform to the ANSI standards prescribed in subsection (c)(1),
    above, provided that the procedures are shall be in substantial conformity
    with those established by the U.S. Department of Transportation under 49
    CFR 325 pursuant to Section 17 18of the Federal Noise Control Act of
    1972, 42 USC U.S.C. §4901 et seq.
     
    32) The Board
    Agency may provide for measurement at distances other than
    the 50 feet specified in 35 Ill. Adm. Code 902.120 through 902.123
    provided that correction factors are applied so that the sound levels so
    determined are substantially equivalent to those measured at 50 feet and
    the measurement distance does not exceed 100 feet. The correction
    factors used shall be consistent with California Highway Patrol Sound
    Measurement Procedures HPH 83.1 (October 1, 1973, as amended
    November 9, 1975), incorporated by reference at Section 900.106.
     
     
    d)
    Procedures Applicable only to 35 Ill. Adm. Code 903
     
    1)
    Measurement procedures for 35 Ill. Adm. Code 903 shall be in
    substantial conformity with ANSI §1.4-1971 Type 1 Precision or Type 2
    General Purpose and ANSI §1.13-1971 - Field Method.
     
    2)
    The Agency may provide for measuring sound emission at distances other
    than 50 feet specified in 35 Ill. Adm. Code 903.162, provided that
    correction factors are applied so that the sound levels so determined are
    substantially equivalent to those measured at 50 feet.
     
    d e) Procedures Applicable only to 35 Ill. Adm. Code 905

     
    19
     
    1) Measurement procedures to determine whether emissions of sound comply
    with 35 Ill. Adm. Code 905.102(a) and 905.103(a)(1) must shall be in
    substantial conformity with the following standards incorporated by
    reference at Section 900.106:ANSI §1.4-1971 Type 1 Precision or Type 2
    General Purpose and SAE Recommended Practice J192a, "Exterior Sound
    Level for Snowmobiles.”
     
    A) ANSI S1.4-1983 (R2001) “American National Standard
    Specification for Sound Level Meters.”
     
    B) SAE Recommended Practice J192 “Exterior Sound Level for
    Snowmobiles.” March 1985.
     
    2) Measurement procedures to determine whether emissions of sound comply
    with 35 Ill. Adm. Code 905.102(b) and 905.103(a)(2) shall be in
    substantial conformity with the following standards incorporated by
    reference at Section 900.106 incorporated by reference at Section 900.106:
    ANSI §1.4-1971 Type 1 Precision or Type 2 General Purpose and SAE
    Recommended Practice J1161, "Operational Sound Level Measurement
    Procedure for Snow Vehicles.”
     
    A) ANSI S1.4-1983 (R2001) “American National Standard
    Specification for Sound Level Meters.”
     
    B) SAE/ANSI Recommended Practice J1161 “Operational Sound
    Level Measurement Procedure for Snow Vehicles.” March 1983.
     
    3) The Agency may establish criteria for measuring at distances other than
    the 50 feet specified in 35 Ill. Adm. Code 905.102 and 905.103, provided
    that correction factors are applied so that the sound levels so determined
    are substantially equivalent to those measured at 50 feet. In adopting new
    or revised criteria, the Agency shall comply with the requirements of the
    Illinois Administrative Procedure Act, [5 ILCS 100] Ill. Rev. Stat. 1985,
    ch. 127, par. 1001 et seq.
     
    (Source: Amended at __ Ill. Reg. ____, effective __________)
     
    Section 900.106 Incorporation by Reference
     
    The Board incorporates the following material by reference. These incorporations include no
    later amendments or editions.

     
    20
    a) American National Standards Institute, 25 West 43rd Street, 4th Fl.,
    New York, New York 10036. (212)-642-4900.
    1) ANSI S1.1-1994 (R1999) “American National Standard Acoustical
    Terminology.”
     
    2) ANSI S1.4-1983 (R2001) “American National Standard Specification for
    Sound Level Meters” and ANSI S1.4A-1985 “Amendment to ANSI S1.4-
    1983.”
     
    3) ANSI S1.6-1984 (R2001) “American National Standard Preferred
    Frequencies, Frequency Levels, and Band Numbers for Acoustical
    Measurements.”
     
    4) ANSI S1.8-1989 “American National Standard Reference Quantities for
    Acoustical Levels.”
     
    5) ANSI S1.11-1986 (R1998) “American National Standard Specification for
    Octave-Band and Fractional-Octave-Band Analog and Digital Filters.”
     
    6) ANSI S1.13-1995 (R1999) “American National Standard Measurement of
    Sound Pressure Level in Air.”
     
    7) ANSI S12.9- 1988 (R1998) “American National Standard Quantities and
    Procedures for Description and Measurement of Environmental Sound -
    Part 1.”
     
    8) ANSI S12.9-1993 (R1998) “American National Standard Quantities and
    Procedures for Description and Measurement of Environmental Sound -
    Part 3: Short-Term Measurements With an Observer Present.”
     
    98) ANSI S12.31-1990 (R2001) “American National Standard Precision
    Methods for the Determination of Sound Power Levels of Broad-Band
    Noise Sources in Reverberation Rooms.”
     
    109) ANSI S12.32-1990 (R2001) “American National Standard Precision
    Methods for the Determination of Sound Power Levels of Discrete-
    Frequency and Narrow-Band Noise Sources in Reverberation Rooms.”
     
    11) International Electrotechnical Commission, IEC 804-2000
    “Integrating/Averaging Sound Level Meters.”
     
    b) Society of Automotive Engineers, 400 Commonwealth Drive, Warrendale, PA
    15096. (877) 606-7323.
     
    1) SAE Recommended Practice J184 “Qualifying a Sound Data Acquisition
    System.” November 1998.

     
    21
     
    2) SAE Recommended Practice J192 “Exterior Sound Level for
    Snowmobiles.” March 1985.
     
    3) SAE/ANSI Recommended Practice J1161 “Operational Sound Level
    Measurement Procedure for Snow Vehicles.” March 1983.
     
    c) California Highway Patrol Sound Measurement Procedures HPH 83.1 (October 1,
    1973, as amended November 9, 1975. Available at Illinois Pollution Control
    Board Clerk’s Office, 100 W. Randolph Street, Suite 11-500, Chicago, IL 60601.
    (312) 814-3620.
     
    (Source: Amended at ___ Ill. Reg. ___, effective _________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE H: NOISE
    CHAPTER I: POLLUTION CONTROL BOARD
     
    PART 903
    RULES AND REGULATIONS FOR THE CONTROL OF NOISE FROM MOTOR RACING
    FACILITIES (Repealed)
     
    SUBPART A: OPERATIONAL PROCEDURES AND RACING WITHOUT MUFFLERS
     
    Section
    903.101 Operational Procedures
    903.102 Racing Vehicles without Mufflers
     
     
    SUBPART B: DRAG RACING FACILITIES
     
    Section
    903.120 Muffler Requirements
    903.121 Sound Level Measurement Requirements
    903.122 Sound Emission Limits
     
    SUBPART C: OVAL RACING FACILITIES
     
    Section
    903.140 Muffler Requirements
    903.141 Sound Level Measurement Requirements
    903.142 Sound Emission Limits
     
    SUBPART D: SPORTS CAR RACING FACILITIES
     
    Section

     
    22
    903.160 Muffler Requirements
    903.161 Sound Level Measurement Requirements
    903.162 Sound Emission Limits
     
    SUBPART E: MOTORCYCLE RACING FACILITIES
     
    Section
    903.180 Muffler Requirements
    903.181 Sound Level Measurement Requirements
    903.182 Sound Emission Limits
     
    SUBPART F: EXCEPTIONS AND COMPLIANCE DATES FOR PART 903
     
    Section
    903.200 Exceptions
    903.201 Compliance Dates for Part 903
     
    APPENDIX A OLD RULE NUMBERS REFERENCED
     
    AUTHORITY: Implementing Section 25 and authorized by Section 27 of the Environmental
    Protection Act (Ill. Rev. Stat. 1981, ch. 111 1/2, pars. 1025 and 1027).
     
    SOURCE: Repealed in R03-8 at ____ Ill. Reg. ___, effective ________________.
     
    SUBPART A: OPERATIONAL PROCEDURES AND RACING WITHOUT MUFFLERS
     
    Section 903.101
    Operational Procedures
     
    The owner or operator of a motor racing facility shall reduce noise emissions from the public
    address system by using noise abatement methods and operational changes -- for example, by
    reducing the volume of the loudspeaker system, by increasing the number of speakers so that the
    volume of individual speakers can be further reduced, and by relocating and redirecting the
    speakers away from residential property.
     
    Section 903.102
    Racing Vehicles without Mufflers
     
    No person shall cause or allow the use or operation of any motor racing vehicle that does not
    require a muffler in accordance with this Part in any motor racing event started after 10:30 p.m.
    local time on any particular weekday or after 11:00 p.m. local time on any particular weekend
    day.
     
    SUBPART B: DRAG RACING FACILITIES
     
    Section 903.120
    Muffler Requirements
     
     

     
    23
    a)
    No person shall cause or allow the use or operation of any drag racing vehicle
    equipped with a normally aspirated gasoline burning engine at a drag racing
    facility unless such drag racing vehicle is equipped with a well-maintained and
    properly installed muffler. Except for any motorcycle used as a drag racing
    vehicle, all mufflers required in accordance with this subparagraph (a) shall meet
    the requirements specified in subparagraph (b).
     
    b)
    Except for any motorcycle used as a drag racing vehicle, all mufflers required in
    accordance with subparagraph (a) shall have noise reducing characteristics which
    will produce a reduction in total vehicle noise of at least the amount listed in the
    following table when such drag racing vehicle is operated in a manner simulating
    wide-open throttle competition. Such noise reduction shall be determined by
    using measurement procedures specified in 35 Ill. Adm Code 900.103.
     
    Total Vehicle Noise Reduction Requirements
    for Mufflers Installed on Drag Racing Vehicles
    (Except Motorcycles) During Wide-open
    Throttle Acceleration Run
     
     
    Type of
    Drag Racing
    Vehicle
    Date Total Vehicle Noise
    Reduction dB
     
    Group A On and after March 15, 1979 Muffler only
    Group A On and after March 15, 1980 10 dB
    Group A On and after March 15, 1983 14 dB
    Group B On and after March 15, 1980 Muffler only
    Group B On and after March 15, 1981 10 dB
    Group B On and after March 15, 1983 14 dB
    Group C On and after March 15, 1981 Muffler only
    Group C On and after March 15, 1982 10 dB
    Group C On and after March 15, 1983 14 dB
     
    1)
    Group A includes all drag racing vehicles in the National Hot Rod
    Association (NHRA) classes of ET Bracket, Stock and Super Stock; the
    International Hot Rod Association (IHRA) classes of ET Bracket, Stock
    and Super Stock; the American Hot Rod Association (AHRA) classes of
    Selectra, Stock, Super Street and Super Stock; and all other similar drag
    racing vehicles.
     
    2)
    Ground B includes all drag racing vehicles in the NHRA class of
    Modified; the IHRA class of Super Modified; the AHRA class of
    Modified/Street; and all other similar drag racing vehicles.
     

     
    24
    3)
    Group C includes all drag racing vehicles in the NHRA classes of
    Competition and Pro Stock; the IHRA classes of Super Comp and Pro
    Stock; the AHRA classes of Top Competition and Pro Stock; and all other
    similar drag racing vehicles.
     
    Section 903.121
    Sound Level Measurement Requirements
     
    a)
    The sound emissions from each drag racing vehicle required to have a muffler in
    accordance with Section 903.120 must be measured before competing in terms of
    A-weighted sound levels using sound level meters in conformance with American
    National Standards Institute (ANSI) Standards §1.4 Type 1 or Type 2
    requirements and using procedures specified in 35 Ill. Adm. Code 900.103. All
    sound level measurements must be made with the microphone one-half meter
    from the exhaust outlet with the engine gear-box in neutral at an engine speed of
    4000 rpm. It shall be the responsibility of the drag racing facility's owners or
    operators, or designated agent, to measure and record the required sound level
    data. Upon reasonable request, the owner or operator shall make such recorded
    sound level data available to the Agency. The owner and operator must keep such
    recorded sound level data for the duration of the racing season.
     
    b)
    The Agency shall publish techniques for determining compliance with Section
    903.120 under static test conditions.
     
    c)
    On and after March 15, 1979, before any motorcycle racing vehicle required to
    have a muffler in accordance with Section 903.120 competes at a drag racing
    facility, the noise emissions from such motorcycle racing vehicle must be
    measured in terms of A-weighted sound levels using sound level meters in
    conformance with ANSI Standards §1.4 Type 1 or Type 2 requirements and using
    procedures specified in 35 Ill. Adm. Code 900.103. The microphone shall be
    located one-half meter from and in the horizontal plane of the rearmost exhaust
    outlet at an angle of 45 degrees behind the exhaust outlet and from the normal line
    of travel of the motorcycle. The engine shall be run with the gear-box in neutral
    at an engine speed equal to one-half of the manufacturer's-recommended-
    maximum-engine-speed. If no manufacturer's-recommended- maximum-engine-
    speed is published for a particular motorcycle, then an engine speed equal to 60
    percent of the engine speed at which maximum horsepower is developed shall be
    used. If no manufacturer's-recommended-maximum-engine-speed is published,
    then the engine speed during the sound level measurement shall be calculated
    from either of the following formulae:
     
    Engine Speed = 306,000
    stroke in millimeters
     
    OR
     
    Engine Speed = 12,000

     
    25
    stroke in inches
     
    Section 903.122
    Sound Emission Limits
     
    On and after March 15, 1979, no person shall cause or allow the use or operation of any
    motorcycle racing vehicle required to have a muffler in accordance with Section 903.120 whose
    sound emissions exceed 115 db(A) when measured in accordance with Section 903.121 and
    when measured one-half meter from the rearmost exhaust outlet.
     
    SUBPART C: OVAL RACING FACILITIES
     
    Section 903.140
    Muffler Requirements
     
     
    a)
    Except as provided in subparagraph (b), no person shall cause or allow the use or
    operation of any oval racing vehicle at an oval racing facility unless such oval
    racing vehicle is equipped with a well-maintained and properly installed muffler.
    Except for any motorcycle used as an oval racing vehicle, all mufflers required in
    accordance with this rule shall meet the requirements specified in subparagraph
    (c).
     
    b)
    The following oval racing vehicles shall not require a muffler in accordance with
    subparagraph (a);
     
    1)
    Sprint racing vehicles;
     
    2)
    Midget racing vehicles;
     
    3)
    Supercharged oval racing vehicles.
     
    c)
    Except for any motorcycle used as an oval racing vehicle, all mufflers required in
    accordance with subparagraph (a) shall have noise reducing characteristics which
    will produce a reduction in total vehicle noise of at least the amount listed in the
    following table when such oval racing vehicle is operated in a manner simulating
    wide-open throttle competition. Such noise reduction shall be determined by
    using measurement procedures specified in 35 Ill. Adm. Code 900.103.
     
    Wide-open Throttle Noise Reduction Requirements
    for Mufflers Installed on Oval Racing Vehicles
    (Except Motorcycles)
     
    Date Muffler Noise Reduction Requirement, dB
    On and after March 15, 1979 Muffler only
    On and after March 15, 1980 10 dB
    On and after March 15, 1982 16 dB
     

     
    26
    Section 903.141
    Sound Level Measurement Requirements
     
    a)
    The requirements for measuring noise emissions from oval racing vehicles, other
    than motorcycles used as oval racing vehicles, shall be identical to those specified
    under Section 903.121(a) for drag racing vehicles.
     
    b)
    The Agency shall publish techniques for determining compliance with Section
    903.140 under static test conditions.
     
    c)
    The requirements for measuring noise emissions from motorcycle racing vehicles
    competing at oval racing facilities shall be identical to those specified under
    Section 903.121(c) for motorcycle racing vehicles competing at drag racing
    facilities.
     
    Section 903.142
    Sound Emission Limits
     
    No person shall cause or allow the use or operation of any motorcycle racing vehicle required to
    have a muffler in accordance with Section 903.140 whose sound emissions exceed 115 dB (A)
    when measured in accordance with Section 903.141 and when measured one-half meter from the
    rearmost exhaust outlet.
     
    SUBPART D: SPORTS CAR RACING FACILITIES
     
    Section 903.160
    Muffler Requirements
     
    a)
    Except as provided in subparagraph (b), on and after March 15, 1979, no person
    shall cause or allow the use or operation of any sports car racing vehicle
    competing at a sports car racing facility unless such sports car racing vehicle is
    equipped with a well-maintained and properly installed muffler.
     
    b)
    The following sports car racing vehicles shall not require a muffler in accordance
    with subparagraph (a): all sports car racing vehicles which are supercharged.
     
    Section 903.161
    Sound Level Measurement Requirements
     
    During all qualifying runs, noise emissions from each sports car racing vehicle required to have a
    muffler in accordance with Section 903.160, must be measured in terms of A-weighted sound
    levels using sound level meters in conformance with ANSI Standards §1.4 Type 1 or Type 2
    requirements and using procedures specified in 35 Ill. Adm. Code 900.103. All measurements
    must consistently be made at the same measurement site; provided, however, that such
    measurement site can be changed if necessitated by good faith circumstances making the use of
    the first measurement site impossible or impractical. It shall be the responsibility of the sports
    car racing facility's owners or operators, or designated agent, to measure and record the required
    sound level data. Upon reasonable request, the owner or operator shall make such recorded
    sound level data available to the Agency. The owner and operator must keep such recorded
    sound level data for the duration of the racing season.

     
    27
     
    Section 903.162
    Sound Emission Limits
     
    No person shall cause or allow the use or operation of any sports car racing vehicle required to
    have a muffler in accordance with Section 903.160 whose sound emissions while accelerating, as
    measured in accordance with Section 903.161, exceed 105 dB (A) when measured 50 feet from
    the center of the lane of travel of such sports car racing vehicle while accelerating on the track.
     
    SUBPART E: MOTORCYCLE RACING FACILITIES
     
    Section 903.180
    Muffler Requirements
     
    a)
    Except as provided in subparagraph (b), on and after March 15, 1979, no person
    shall cause or allow the use or operation of any motorcycle racing vehicle
    competing at a motorcycle racing facility unless such motorcycle racing vehicle is
    equipped with a well-maintained and properly installed muffler.
     
    b)
    The following motorcycle racing vehicles shall not require a muffler in
    accordance with subparagraph (a): supercharged motorcycle racing vehicles.
     
    Section 903.181
    Sound Level Measurement Requirements
     
    The requirements for measuring noise emissions from motorcycle racing vehicles competing at
    motorcycle racing facilities shall be identical to those specified under Section 903.121(c) for
    motorcycle racing vehicles competing at drag racing facilities.
     
    Section 903.182
    Sound Emission Limits
     
    No person shall cause or allow the use or operation of any motorcycle racing vehicle required to
    have a muffler in accordance with Section 903.180 whose sound emissions exceed 115 dB (A)
    when measured in accordance with Section 903.181 and when measured one-half meter from the
    rearmost exhaust outlet.
     
    SUBPART F: EXCEPTIONS AND COMPLIANCE DATES FOR PART 903
     
    Section 903.200
    Exceptions
     
    a)
    Sections 903.120 through 903.182 shall not apply to any special-motor-racing-
    events, provided that not more than three special-motor-racing-events are
    conducted at any motor racing facility during any calendar year. The owner or
    operator of any motor racing facility which is conducting a special-motor-racing-
    event must previously notify the local public that a special-motor-racing-event
    will be conducted.
     
    b)
    Sections 903.120 through 903.182 shall not apply to motor racing facilities which
    conduct motor racing events on fewer than five days per calendar year.

     
    28
     
    c)
    Sections 903.120 through 903.182 shall not apply to fairground motor racing
    facilities during motor racing events held in conjunction with a state or county
    fair.
     
    d)
    Sections 903.102 through 903.182 shall not apply if there are no residential
    dwelling units within two miles of such motor racing facility's racing surface.
     
    e)
    Sections 903.102 through 903.182 shall not apply to any motor racing facility
    whose sound emissions do not at any time exceed the background sound level by
    more than 7 dB(A) at any residential dwelling unit.
     
    f)
    Sections 903.102 through 903.182 shall not apply to any existing motor racing
    facility whose sound emissions do not at any time exceed the allowable octave
    band sound pressure levels specified in 35 Ill. Adm. Code 901.102(a) when
    measured at any point within any receiving Class A land.
     
    g)
    Sections 903.102 through 903.182 shall not apply to any new motor racing facility
    whose sound emissions do not exceed at any time during daytime hours the
    allowable octave band sound pressure levels specified in 35 Ill. Adm. Code
    901.102(a) or at any time during the nighttime hours the allowable octave band
    sound pressure levels specified in 35 Ill. Adm. Code 901.102(b) when measured
    at any point within any receiving Class A land.
     
    Section 903.201
    Compliance Dates for Part 903
     
    a)
    Every owner or operator of an existing motor racing facility shall comply with the
    requirements of this Part by September 24, 1978.
     
    b)
    Every owner or operator of a new motor racing facility shall comply with the
    requirements of this Part when motor racing activities commence at such new
    motor racing facility.
     
    Section 903.APPENDIX A
    OLD RULE NUMBERS REFERENCED
     
    The following table is provided to aid in referencing old Board rule numbers to section numbers
    pursuant to codification.
     
    Old Part 4 of Chapter 8 35 Ill. Adm. Code Part 903
     
      
    Rule 401 Section 903.101
    Rule 402 Section 903.102
    Rule 403 Section 903.120
    Rule 404 Section 903.121
    Rule 405 Section 903.122
    Rule 406 Section 903.140

     
    29
    Rule 407 Section 903.141
    Rule 408 Section 903.142
    Rule 409 Section 903.160
    Rule 410 Section 903.161
    Rule 411 Section 903.162
    Rule 412 Section 903.180
    Rule 413 Section 903.181
    Rule 414 Section 903.182
    Rule 415 Section 903.200
    Rule 416 Section 903.201
     
    IT IS SO ORDERED.
     
    I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the Board
    adopted the above opinion and order on June 5, 2003, by a vote of 6-0.
     
     
      
      
      
      
      
     
    Dorothy M. Gunn, Clerk
    Illinois Pollution Control Board
     
     
     

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