ILLINOIS POLLUTION CONTROL BOARD
    April
    8,
    1976
    HYON WASTE MANAGEMENT SERVICES,
    INC.
    Petitioner,
    )
    v.
    )
    PCB 75—413
    ENVIRONMENTAL PROTECTION AGENCY,
    Respondent.
    Mr. George Bullwinkel, Attorney, appeared for the Petitioner;
    Mr. Peter E,
    Orlinsky, Attorney, appeared for the Respondent.
    OPINION AND ORDER OF THE BOARD
    (by Mr.
    Zeitlin):
    This matter is before the Board on a Permit Appeal Petition
    filed by Petitioner Hyon Waste Management Services,
    Inc.
    (Hyon) on
    October
    22,
    1975.
    The Environmental Protection Agency
    (Agency)
    filed
    its
    record of permit application on December
    2,
    1975.
    Hearings
    were held in the matter on January 26 and 27, 1976 in conjunction
    with another Hyon Permit Appeal, PCB 75—457.
    (PCB 75—413 and 75—457
    are not consolidated cases.
    An Interim Order of the Board dated
    December
    11,
    1975,
    specifically denied a Motion for Consolidation.
    To avoid duplication of effort,
    however, the January
    26 and 27
    hearings were held to jointly consider the two matters;
    this case,
    like PCB
    75-457,
    is decided on the combined Record.)
    This case concerns Hyon’s attempt
    to obtain an operating permit
    for an incinerator used at Hyon’s Chicago facility,
    located on the
    shore of Lake Calumet,
    on the city’s south side.
    Characterized by
    Petitioner as an “integrated treatment facility for industrial wastes,”
    (R.6),
    Ilyon’s Chicago plant has facilities
    for the treatment, disposal,
    destruction,
    or other elimination of many kinds of industrial liquid
    wastes,
    (e.g.,
    R.62—72,
    93,
    98,
    200).
    Approximately 40—50,000 gallons
    of various types of waste are
    treated or otherwise disposed of at
    the Hyon plant,
    (R.57).
    Hyon’s application to the Agency for an operating permit under
    Ch.
    2: Air Pollution,
    of the Board’s Rules and Regulations, for the
    incinerator at the Chicago plant was submitted on July 18,
    1975,
    (Hyon,
    Ex.15).
    That permit application was denied by the Agency
    in
    a letter dated October 15,
    1975,
    (Hyon,
    Ex.l6).
    Following is
    the reason given by the Agency for that denial:
    The liquid waste incinerator operating at 4500
    pounds per hour of liquid waste is allowed to
    emit up to 0.08 gr/scf adjusted to 12
    CO2.
    Your permit indicates that up to 0.198 gr/scf
    adjusted to 12
    CO2 may
    be emitted.
    This
    amount is
    in excess of the amount allowed.
    21—75

    —2—
    This
    is not the first time that Hyon’s incinerator has been
    before this Board on a Permit Appeal.
    On February
    27,
    1975 we
    entered an Order dismissing as moot a similar Permit Appeal filed
    November 20, 1974; however,
    that Order also granted Hyon Variances
    for its incinerator from Rules
    103(a),
    103 (b)
    ,
    202 (b)
    ,
    and 203 (e) (2)
    of Chapter
    2.
    Iyon
    Waste Management Services,
    Inc.
    v.
    EPA, PCB 74-433,
    15 PCB 605
    (1975)
    (Supplemental Statement by Mr. Dumelle,
    15 PCB 609).
    The background information given
    in the Board’s Opinion there
    is,
    however, disputed in this case; our decision on those disputed facts
    will,
    in part,
    be determinative of the issues
    in this case.
    In addition,
    the Board’s assumptions
    in granting the Variances in
    PCB 74-433, particularly with regard to the applicability of Rule
    203(e) (2)
    to Hyon’s incinerator, are also in issue here.
    The issues in this case are twofold:
    1.
    Is the particulate limitation of Rule
    203 (e) (2) applicable to the type of incinerator
    operated by Hyon at its Chicago facility?
    2.
    If the particulate limitations of Rule
    203(e) (2)
    are indeed applicable, was the Agency’s
    rejection of Hyon’s permit application proper?
    The pleadings, exhibits, and testimony offered by the parties
    with regard to the second of those issues were highly complex and
    technical.
    These included discussions of the propriety of applying
    the
    12 per cent carbon dioxide correction in Rule 203 (e) (2)
    to an
    incinerator like Hyon’s,
    the possibility or propriety of making
    fuel-based adjustments to arrive at such a correction factor,
    and
    various questions concerning the acceptability of certain stack
    testing procedures.
    DISCUSSION
    The Rules and Regulations Governing the Control of Air Pollution,
    promulgated by the Air Pollution Control Board, defined an incinerator
    as a,
    Combustion apparatus designed for high temperature
    operation in which solid,
    semi-solid,
    liquid, or
    gaseous combustible wastes are ignited and burned
    efficiently and from which the solid residues contain
    little or no combustible material.
    §
    1,
    Definitions.
    21
    76

    —3—
    When the Board enacted its own emission Regulations for
    incinerators
    (which include limitations other than those for particu-
    lates under Rule 203),
    it defined “incinerator” as a, “cJombustion
    apparatus in which refuse is burned.”
    PCB Regs., Ch.
    2,
    Rule 201,
    Definitions.
    No further reference was made to that definition in
    the accompanying Opinion, which stated that the definitional section
    of the Regulations
    is
    “largely self-explanatory.”
    In the Matter of
    Emission Standards,
    R
    71-23
    (April
    13,
    1972), Opinion at 12.
    Nor
    was any further explanation of the definition given elsewhere in
    the Regulations themselves or in other sections of the Board’s Opinion.
    In attempting to determine the Board’s intended coverage in
    that definition, we must examine,
    first, possible refinement of this
    definition;
    and second, the Board’s concept of what was to be achieved
    under the Regulations limiting emissions from incinerators.
    When the Board promulgated its definition of “incinerator,”
    the term “refuse” was
    itself defined
    in the Environmental Protection
    Act as,
    “any garbage or other discarded solid materials.”
    Ill.
    Rev.
    Stat.,
    Ch.
    111-1/2,
    §1003(k)
    (1975).
    It would seem from that refine-
    ment of the “incinerator” definition that the incinerators controlled
    by Rule 203(e)
    are limited to those in which “garbage or other...
    solid materials”
    is burned.
    However, as the Agency points out
    in its Brief,
    the Illinois
    Legislature changed the Environmental Protection Act’s definition of
    “refuse” in 1975.
    Illinois Public Act 79—762
    amended the definition
    in
    §3(k) of the Act to include,
    “any garbage or other discarded
    materials with the exception of
    certain
    radioactive materials
    3
    .
    .
    .
    In light of that redefinition by the Legislature, the Agency argues
    that the definition of an incinerator controlled by our Regulations
    now includes one which burns either liquid or solid waste.
    Hyon,
    however, argues that the Board’s definition of “incinerator” must
    use the word “refuse”
    as it was defined when the definition of
    “incinerator” was written, i.e.,
    solid materials only.
    We find that Hyon’s contention is correct.
    The Agency’s attempt
    to distinguish the cases cited by Petitioner on the subject of statu-
    tory interpretation is incorrect.
    The Agency’s statement that these
    cases would not apply because the terms here are not “subject to
    unclear meanings or gradually changing usages,”
    (EPA Brief, at
    5),
    begs the question:
    As the Agency also points out, the definition
    actually has changed.
    21—n

    —4—
    Nor do we feel that the Legislature’s change in definition
    reflects any conscious attempt to affect the coverage of our Air
    Pollution Regulations as they relate to refuse or incinerators.
    No
    such intent
    is expressed in the new definition.
    Without such express
    intent, we find that the general rule of statutory interpretation,
    giving to words of art or words subject to changing definitions, the
    definition in effect at the time of enactment is controlling.
    Even without that statutory interpretation, there are other
    compelling arguments presented by
    Iiyon which would lead us to the
    same conclusion,
    i.e.,
    that Rule 203(e)
    applies only to incinerators
    burning primarily solid waste.
    First, what little guidance which does exist in the Opinion
    accompanying the Emission Regulations
    is found
    in the section accom-
    panying Rule 203(e)
    itself.
    As pointed out by Hyon,
    the Board there
    stated that the particulate limitation of 0.08 gr/scf for incinerators
    “tracks the Federal New Source Standards.
    ..
    .“
    R 71—23,
    supra,
    citing
    40 CFR §60.51.
    The Federal New Source Standards definitions, id.,
    specifically limit
    the coverage of “incinerators” to those
    “buF~iTng
    solid waste,”
    “solid waste” itself being defined as “refuse, more
    than 50
    of which is municipal type waste consisting of
    a mixture
    of paper, wood,
    yard wastes,
    food wastes,
    plastics, leather, rubber,
    and other combustibles, and noncombustible materials such as glass
    and rock.”
    Were our own standards
    to
    include in their definition
    of “incinerators” those burning largely liquid wastes, they would
    hardly “track” the Federal New Source Standards.
    Second, Hyon argues persuasively that the correction factor
    in Rule 203 (e) (2),
    to 12
    CO2, would be inappropriate for application
    to incinerators burning largely liquid wastes of the type burned
    in
    Hyon’s incinerator.
    There was considerable discussion of this issue
    at the hearings,
    (eg.,
    R.
    145—147,
    205—209,
    215,
    225,
    228, 372—373),
    and in both parties’
    Briefs.
    Although portions of that discussion
    concerned correction factors to be applied if the Board were to
    decide that Rule 203(e) (2) did apply
    to Ryan’s facility, the discussion
    is nonetheless applicable h~.
    The sum of those discussions at hearing indicates that the
    particulate limitations of Rule 203(e) (2) were based, particularly
    with regard to the 12
    CO7 correction factor on emissions likely
    to be generated from the burning of solid waste, whether those likely
    emissions are generated from burned coal
    (as Ryan attempted to show
    at hearing,
    R.144),
    or from municipal wastes
    (as exemplified by the
    definitions cited above in the Federal New Source Standards).
    The
    Agency’s contrary argument, to the extent that it is not empowered
    to compensate whether a Regulation is to
    a source’s “advantage or
    disadvantage”
    is inapropos.
    Petitioner properly shows that,
    under
    such an application of the Rule,
    it is conceivable that under certain
    conditions, with certain fuels,
    no particulate emissions would be
    allowed.
    While a laudable goal,~urRegulations cannot, as presently
    constituted, be construed in such a manner.
    21 —78

    —5—
    Similarly, the Agency’s argument that Ryan’s proper relief
    in this regard should be a Petition for regulatory change is not
    applicable here.
    Our Regulations do not require that every imagi-
    nable source be covered under the existing emission limitations.
    Where the existing Regulations do not provide for a specific limi-
    tation, we need not apply a tangential limitation due to that lack
    of provision.
    We find no foundation for the Agency’s statement that,
    “the
    Board’s particulate regulations are intended to cover all particulate
    sources,”
    (Brief,
    p.
    7), which is cited only to §9(a) of the Act.
    To agree with that statement is tantamount to proclaiming our oinni-
    science, particularly when the statement is viewed in light of the
    Act’s requirement that the Board examine technical and economic
    feasibility in enacting Regulations.
    Raving decided that the particulate limitations of Rule 203(e) (2)
    were meant to apply to incinerators burning solid wastes,
    and not
    liquid wastes, we must then determine the nature of Hyon’s incinerator.
    Neither of the parties dispute the fact that what Ryan operates
    is an “incinerator,”
    in the sense of it being used to burn wastes,
    (e.g.,
    R.90,
    158,
    180).
    Arguing that Rule 203(e) (2) must therefore
    be applicable,
    the Agency cites the recent case of People and EPA v.
    Ruben Metal Co.,
    Inc., P03 75-20
    (Supplemental Opinion,
    Jan.
    14,
    1976),
    whicth stated that “in determining which emission standard would apply
    to a given
    ‘incineration’
    source,
    the primary purpose of that source
    is determinative. The determination of what
    is the primary purpose of
    the source must be made on a case by case basis.”
    While the primary purpose of Hyon’s incinerator is
    certainly
    ‘incineration,’
    as the word was used in Ruben, the primary purpose
    here is actually the incineration of liqufd wastes. As a result,
    the particulate emission limitations of Rule 203 (e)
    (2)
    do not apply
    to Hyon’s “incinerator.”
    The Agency argues that the Record does not show the proportion
    of liquid to solid wastes incinerated by Ryan, and that Rule 203(e) (2)
    should apply unless no solid wastes are burned.
    However, such an
    analysis
    is contradi~toryto that in Ruben,
    supra.
    The Record in
    this case makes
    it clear that the primary purpose of Hyon’s incine-
    rator is the destruction of liquid wastes,
    (e.g.,
    R.132,
    133,
    158).
    In light of all of the above, we find that the particulate
    limitation of I~u1e203(e) (2)
    is inapplicable in Hyon’s case.
    Each
    of the grounds put forward by Ryan for this decision would be suffi—
    cient, individually; collectively, they are compelling.
    21—79

    —6—
    Our decision to this effect troubles us.
    It
    is evident that
    some control over the incineration process operated by Hyon is
    necessary; the materials destroyed in Hyon’s incinerator are certainly
    capable, as the Agency points out,
    of causing considerable environ-
    mental and public health damage.
    It
    is unfortunate that Hyon’s
    operations are not, as the Agency would have
    it, controlled by our
    particulate Regulations.
    But, as is pointed out above, we are unable
    to find any real relationship between those Regulations and Hyon’s
    operations.
    This decision is not a
    “free ticket” for Ryan, however.
    Ryan
    remains bound by the provisions of the Act and our Regulations
    prohibiting air pollution.
    In addition, Hyon’s incinerator remains
    subject, as an “emission source,” to the operating permit requirement.
    We would hope that,
    to obtain the protection of S49(e)
    of the Act,
    Ryan will itself propose applicable regulations.
    We likewise hope
    that the Agency will either propose such Regulations or provide
    guidance and technical assistance to the Board in its consideration
    of any other proposal, whether from Hyon or some other source.
    This Opinion constitutes the findings of fact and conclusions
    of law of the Board in this matter.
    ORDER
    IT IS THE ORDER OF THE POLLUTION CONTROL BOARD that the decision
    of the Environmental Protection Agency, dated October 15,
    1975,
    denying Petitioner Ryan Waste Management,
    Inc., an operating permit
    for its liquid waste incinerator,
    be reversed, and that said Petitioner
    is entitled to an operating permit therefor.
    Mr.
    James Young and Mr. Jacob Dumelle abstained.
    I, Christan L. Moffett, Clerk of the Illinois Pollution
    Control Board, heç~ycertify the
    bove Opinion and Order were
    adopted on the
    ~‘
    day of
    _________,
    1976, by a vote of
    3-~
    stan
    Illinois Pollution
    21—80

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