ILLINOIS POLLUTION CONTROL BOARD
    January
    16, 1973
    ENVIRONMENTAL PROTECTION AGENCY
    ~72—l80
    v
    NYSTIK TAPE, A DIVISION OF BORDEN,
    INC.,
    )
    a New Jersey Corporation,
    Qualified
    To
    Do Business
    in Illinois
    RICHARD W.
    COSBY AND DOUGLAS
    T. MORING,
    ASST.
    ATTORNEYS GENERAL,
    ON BEHALF OF ENVIRONMENTAL PROTECTION AGENCY
    JAMES
    W.
    KISSEL AND THOMAS
    N. McMAHON
    OF SIDLEY
    & AUSTIN,
    ON
    BEHALF
    OF RESPONDENT
    OPINION AND ORDER OF THE BOARD
    (BY SAMUEL
    T.
    LAWTON,
    JR.):
    Amended complaint was filed by the Environmental
    Protection Agency
    against Mystik Tape,
    a corporate division of Borden,
    Inc., Respondent,
    alleging that Respondent’s plant has emitted odor—producing gases and
    other contaminants and thereby caused air pollution
    in violation of
    Section
    9(a)
    of the Environmental
    Protection Act and that Respondent
    installed new equipment capable of causing or contributing
    to air pollu-
    tion or designed to prevent air pollution without having first obtained
    permits from the Agency,
    in violation of Section
    9 (b)
    of the Act and Rule
    3-2.110 of the Rules and Regulations Governing the
    Control of Air Pollu-
    tion
    (Air Rules)
    -
    We find that the evidence sustains the allegations
    of the complaint with respect to the causing of air pollution as defined
    in the Act and that Respondent has
    failedtô
    obtain permits
    in violation
    of the Act and the Air Rules.
    We assess
    a penalty for said violations
    and require the institution of an abatement program, all as more fully
    set forth below.
    Before considering the merits of the case,
    it is necessary to
    dispose of certain procedural matters raised by the pleadings and
    motions filed.
    The Agency’s original complaint was filed on April
    27,
    1972.
    On June 8, an amended complaint was filed without objection by
    Respondent
    to plead more specifically the assertions with regard to
    the permit violations.
    Odor and air pollution violations occurring
    between July
    1,
    1970 and the date of the filing of the complaint were
    asserted.
    On August 30, the Agency filed a second amended complaint
    alleging violation Of Section
    9 (a)
    “during the period beginning
    July
    1,
    1970 and continuing each day of operation until the close of
    the
    record
    herein.”
    (Emphasis added).
    To this,
    Respondent objected
    and moved that evidence of violation subsequent to June
    8, 1972 be
    excluded from the record.
    The Hearing Officer permitted such evidence
    d
    503

    to be presented during the hearing but referred the decision as to
    its admissibility to the Board
    (R.
    481).
    We grant respondent ‘s motion
    in this respect.
    Hearings were held on the First Amended Complaint on August 18,
    19,
    September
    8,
    16,
    29, October
    10 and 30,
    1972.
    The filing of a
    Second Amended Complaint after the beginning of the hearings in the
    form submitted presents a recurring issue that must be disposed of
    for the protection of the interests of all parties concerned.
    The
    complainant has alleged violation of Section
    9(a)
    “continuing until
    the close of the record”.
    This would include violations subsequent
    not only to the filing of the complaint but also beyond the commence-
    ment of the hearings.
    The admission of such evidence would create an
    impossible burden for Respondent
    in the preparation of its case.
    Adequate preparation would be virtually impossible
    if the parties are
    expected to respond to unspecified events occurring subsequent
    to the
    initiation of the proceeding.
    The Board
    is being faced with increasing
    frequency with pleadings alleging violations continuing “to the close
    of the record.”
    Sometimes,
    as in the present case,
    it
    is
    in the form
    of an amendment to the complaint subsequent to the commencement of
    hearings and justification for the practice, premised on the ability
    to cause pleadings to conform to the proof.
    However, even this is
    questionable, because at the time of the pleading some of the alleged
    events of violation may not have yet taken place.
    The concept of allowing pleadings to be amended to conform to
    proof was never intended to permit omnibus assertions of unspecified
    violations that may occur in the future.
    If events have taken place
    since the original filing of the complaint that the Agency wishes
    to
    assert as violations, the Agency should move that the complaint be
    amended to include those offenses before making proof of such violations.
    The Respondent would then be forewarned of what it was being charged with
    and would have an adequate opportunity to prepare its defense.
    Shot-
    gun assertions of future violations will no longer be tolerated.
    This
    does not foreclose some latitude in the showing of continuing violations
    for purpose of imposition of penalties or promulgation of abatement
    programs.
    Likewise, while we do not look with favor upon generalized
    allegations of violations
    covering a specified period of time,
    as dis-
    tinguished from detailed specification of alleged offenses, such method
    of pleading is not fatally defective if it relates to
    a period in the
    past.
    Particularization needed by Respondent can be obtained by use
    of pre—trial discovery processes
    if it desires.
    However, allegations
    of offenses for periods projecting into the future will no longer
    be tolerated.
    For purposes of determining violation of the Act and
    regulations in the present case, consideration of all allegations and
    proof relating to periods beyond the filing of the amended complaint
    will be excluded for purposes of determination of violation.
    Allega-
    tions and proof relating to periods prior to June 8,
    1972,
    the date of
    the filing of the first ~amended complaint, will be the only allegations
    considered by the Board for determination of violation.
    Accordingly,
    admission of the second amended complaint will be denied.
    —2—
    6
    504

    The Mystik Tape plant
    is located in Northfield, Illinois.
    The area surrounding the plant
    is mixed residential,
    industrial
    and commercial with
    a
    high
    school adjacent to the plant property.
    In 1953,
    the first plant, containing 23,000 square feet, was
    constructed on a
    20 acre tract.
    Subsequently, additions
    to the
    plant were made as follows:
    83,000 square feet in 1960,
    82,000 square feet in 1964,
    23,000 square feet in 1965 and
    89,000 square feet in 1970
    (R. 766—767)
    .
    In 1963,
    seven acres
    of Respondent’s property was condemned for construction of the
    high school.
    The high school buildings and playing fields lie
    directly east of Respondent’s plant.
    There is testimony that citizens were affected by noxious
    odors emitted from the plant prior to 1970.
    (R. 127-l3G)
    .
    Other
    witnesses provided records indicating that there were numerous
    days between January, 1970 and June
    8, 1972 when they were aware
    of noxious odors being emitted from the Mystik plant.
    (R. 101-11,
    211—39,
    290—321,
    321—369, 369—410,
    410—448a, 448b—477, 622—690).
    All witnesses identified the Mystik plant as the source of these
    odors and were positive of the source.
    They based their certainty
    on wind direction, visual observation and inspection of surrounding
    area.
    They characterized the odor variously as “rubber or burning
    rubber”
    (R.
    248),
    “heavy or acrid like a new plastic object or
    magic marker”
    (R.
    299),
    “sweet and strong”
    (R.
    324),
    “sickeningly
    sweet and burning”
    (R.
    372),
    “burning”
    CR.
    422),
    “sharp, acrid,
    smelling like burning adhesive”
    (R.
    457),
    “sweet”
    (R.
    493),
    “strong,
    penetrating and pungent”
    (R.
    630-31).
    The witnesses
    described their reactions as changing from “feeling nauseated”
    (R.
    468)
    to “having a burning sensation when inhaling”
    (R.
    422)
    to causing
    “watery eyes”
    (R.
    373)
    to producing “headaches
    arid
    sore throats.”
    The witnesses were able to characterize oth~r
    sources of odor and differentiate them from that attributed to
    respondent.
    The odor prevented residents from using their yards
    (R.
    377)
    and interfered with their indoor life when the windows
    were open
    (R.
    296).
    The odor did not appear to cause any property
    damage or to force people to seek medical treatment.
    However,
    there
    is no question that the odors interfered with the comfort
    and enjoyment of life of the nearby residents, and constituted
    a nuisance and violated Section
    9
    (a)
    of. the act prohibiting the
    causing of air pollution.
    Respondent concedes that it emits odors from its plant but
    disputes the effect of the pdors on those who live and work in
    the surrounding area.
    There has been correspondence between the
    Respondent and the Village of Northfield respecting odors from
    the plant
    (Complainant’s Exhibits 15 through 19).
    Further,
    Respondent has met with citizens of the area and students from the
    high school on one or more occasions
    to assure them that the
    Company was attempting to deal with the problem
    CR. 117-119).
    There is indication of improvement in the situation
    ir recent months.
    —3—
    6
    505

    In 1970, Respondent installed
    two
    separate “odor counteractant”
    devices on its facilities.
    The purpose of the devices was to absorb
    or counteract any of the odors that might be emanating from the pro-
    cess
    (R.
    275).
    A device known as Air-Chem was installed in the ex-
    haust vent
    CR.
    281).
    In August of 1970,
    a device known as Chem-
    Screen was installed on the roof
    CR.
    274), covering approximately
    one—half of the roof area and intended to operate as an air—curtain
    forcing any odors
    to pass through a curtain of odor—counteractant
    CR. 274-76).
    The odor-counteractant material has an odor of its
    own
    (R.
    278).
    In early 1971, Respondent began installation of its
    “No.
    9
    spreader”,
    a coating line where adhesive is applied to a material
    backing to create an adhesive tape
    CR.
    273).
    Installation was
    completed in October of 1971.
    This spreader,
    to be discussed in
    greater detail below,
    is presently responsible for over one—half
    of
    the production of the Mystik plant in square yards of pressure-
    sensitive tape.
    (R.
    801).
    Subsequent to the start of construction
    of the No.
    9 spreader, Respondent applied to the Agency for con-
    struction permits for its No.
    9 spreader and an oder—counteractant
    device.
    In October 1971,
    the Agency denied both permits
    CR.
    49).
    The
    permit for the oder counteractant device was denied because the
    Agency believed it was not intended to reduce or prevent odor but
    only to perfume or mask the odor.
    CR.
    46).
    The other permit was
    denied because the Agency believed that the spreader was a potential
    source of air pollution and therefore, needed an accompanying
    pollution control device
    CR.
    52).
    Correspondence between the Agency and the Respondent ensued
    in which Respondent indicated its willingness to comply with any
    criteria the Agency supplied.
    CR.
    58-60).
    Respondent also
    indicated that it believed it did not need a construction permit
    for either device.
    CR. 64-66).
    The Agency stated that the operation
    of the devices contributed
    to air pollution and would violate the
    Act,
    and that technical information should be submitted on the
    device’s operation.
    The Agency also requested that calculations
    and actual experimental
    tests with technical reference be included.
    CR. 66-67).
    A subsequent meeting in Springfield took place between
    the parties.
    Another application for permit was filed for the
    spreader which was denied on March
    20, 1972
    (R.
    49),
    because of
    potential emissions from the new equipment.
    (Complainant’s
    Exhibits 4 and 5).
    Respondent contends that a construction permit for the devices
    described above is not necessary.
    It
    is Respondent’s posititon
    that:
    1.
    The original Illinois Air Pollution Control Act does not
    authorize any regulation in regard to air pollution control
    devices such as the odor counteractant devices under
    consideration.
    —4—
    6— 506

    2.
    Section
    3-2.110
    is
    invalid
    because
    it requires permits
    for air pollution control equipment which is not
    authorized by the Air Pollution Control Act.
    3.
    Section
    9
    Cb)
    of the Environmental Protection Act requires
    permits for equipment designated by the Board regulations.
    4.
    Rule 103 of the Air Pollution Control Regulations being
    the only applicable regulation applies only to specified
    air contaminants
    of which there is no proof of emissions
    by Respondent.
    We find the contentions of Respondent wholly lacking in
    merit.
    The power to regulate air pollution control devices has
    been within the scope of powers of administering boards since the
    promulgation of the Air Pollution Control Act.
    This power has in
    no way been diminished by the Environmental Protection Act or the
    regulations of this Board.
    Under the Air Pollution Control Act
    (Chapter 111-1/2 Illinois
    Revised Statute,
    Section 240.2,the following definitions appear~
    (a)
    “Air contaminant”
    is particulate matter,
    dust,
    fumes, gas,
    mist,
    smoke,
    or vapor, or any combination thereof.
    Cb)
    “Air contaminant source”
    is any and all sources of
    emissions of air contaminants, whether privately or publicly owned
    or operated.
    Without limiting the generality
    of the foregoing,
    this term includes all types of business, commercial and industrial
    plants, works, shops and stores, and heating and power plants and
    stations, building and other structures of all types,
    including
    single and multiple family residences,
    apartments, houses, office
    buildings,
    hotels, restaurants,
    schools, hospitals,
    churches and
    other institutional buildings,
    automobiles,
    trucks,
    tractors,
    buses
    and other motor vehicles,
    garages and vending and service locations
    and stations,
    railroad locomotives,
    ships, boats and other water-
    borne craft, portable fuel—burning equipment,
    incinerators of all
    types, indoor and outdoor, refuse dumps and piles, and all stack
    and other chimney outlets from any of the foregoing.
    Cc)
    “Air
    Pollution”
    is
    presence
    in
    the
    out—door
    atmosphere
    of
    one
    or
    more
    air
    contaminants
    in
    sufficient
    quantities
    and
    of
    such
    characteristics and duration as to be injurious to human, plant or
    animal life or to property,
    or which unreasonably interfere with
    the
    enjoyment of life and property.
    Section 240.5 provided as follows:
    “It is the intent a,nd purpose of this Act to maintain purity of
    the air resources of the State consistent with the protection of the
    normal health,
    general welfare and physical property of the people,
    —5—
    6— 507

    maximum
    employment
    and
    the
    full
    industrial
    development of the
    State.
    The Board shall seek the accomplishment of these objectives
    through the prevention, abatement and control of air pollution by
    all practical and economically feasible methods.”
    From the foregoing statutory provisions, it is clear that the odor
    producing facilities of Respondent and specifically,
    its spreader
    equipment,
    stacks and other sources of emission, constitute air con-
    taminant sources.
    The installation of odor abatement equipment on
    such sources becomes an inherent part of the sources.
    The totality
    of the equipment,
    stack or emission source constitutes~installation
    of new equipment capable of becoming a source of pollution.
    Section
    240.5-1.2 permits adoption of regulations consistent with the general
    intent and purposes of the Act which include, but are not limited to,
    installation of new equipment capable of becoming a source of air
    pollution.
    Improperly installed or operating abatement equipment
    on an air contaminant source could become a source of air pollution.
    Section 3-2.110 of the Air Rules adopted pursuant to statutory
    authority provides as follows:
    “A permit shall be required from the Technical Secretary for
    installation or construction of new equipment capable of emitting
    air contaminants
    to the atmosphere and any new equipment intended for
    eliminating, reducing or controlling emission of air contaminants.”
    This provision
    is
    in implementation of the foregoing statutory
    provisions and expressly provides for the installation of new equip-
    ment intended for the eliminating, reducing or controlling of air
    contaminant emissions.
    Section 9Cb) of the Environmental Protection Act provides that
    no
    person
    shall:
    “Construct, install,
    or operate any equipment,
    facility, vehicle,
    vessel or aircraft capable of causing or contributing to air pollution
    or designed to prevent air pollution of any type designated by Board
    regulations, without a permit granted by the Agency,
    or in violation
    of any conditions imposed by such permit.”
    Section
    49 Cc)
    of the Act keeps in force and effect all pre-
    vious regulations of the Air Pollution Control Board, including those
    presently under consideration until repealed, amended, or superceded
    by new regulations.
    Installation of the equipment with respect to
    which violations are asserted pre-dated the new air pollution regulations,
    and arguments that the new Regulation 103 supercedes Section 3-2.110
    even if correct,
    would not be available to Respondent for installations
    having taken place prior to the effective date of this regulation.
    Likewise, while it is not controlling to the case,
    the odor counterac—
    tant installations are themselves capable of emitting odors which would
    —6—
    6
    508

    make them potential sources of air pollution,
    and, accordingly,
    subject to the provisions of the regulation.
    Accordingly, we find that
    Respondent’s
    failure to obtain permits for the installation of the odor
    abatement equipment constituted a violation of Air Rules, Section 3—2.
    110 and Section 9(b) of the Act.
    Respondent made application to the
    Agency for permit covering its odor abatement devices in apparent recog-
    ition that permits were required for these devices under the relevant
    ules and statutory provisions.
    Once having pursued the permit process,
    ~espondent should have continued with it pursuant to the statutory
    framework.
    After having received a rejection of the permit applications
    y the Agency, Respondent should have appealed the decision to the Board.
    E’his would have properly brought the issue before the Board for deter-
    nination as to whether the Agency’s position was correct and conceivably
    resulted in an agreement as
    to the cause and source of the odor.
    Respon—
    sent’s failure to follow the statutory procedures suspended the ultimate
    determination an inordinate length of time and led to the events that
    culminated in the present proceeding.
    Respondent is in the midst of a program which will result in the
    replacement of all photo-chemically reactant solvents by June of 1973
    (R.
    1090)
    .
    All odor counteractant devices have been shut down.
    Odor
    counteractants are being mixed into the adhesive process to achieve a
    stoichiometrically balanced reaction
    (R. 1138).
    In addition, Respondent
    is developing
    a
    “hot melt”
    process which would use no solvents
    (R. 1091).
    It believes that this process would provide substantial savings if the
    process
    is implemented.
    The preceeding makes plain that the Company has been aware of the
    existence of the odor problem for a substantial period of time.
    It has
    attempted,
    and is attempting, to cope with the problem by a variety of
    methods.
    Good faith has been demonstrated in this respect.
    Respondent’s technical expert, a chemical engineer now employed
    as Environmental Engineering Manager for the parent corporation, testi-
    fied
    that
    the odor problem has been isolated.
    Six basic tapes were
    found to be stronger in odor than other basic tapes by a significant
    margin
    (R.
    1119).
    Particular processes that have been a source of the
    odor have been isolated,
    namely, the cure zones of the higher temperature
    zones of the ovens and in some cases, the release coat zones
    (R. 1071—
    72).
    Respondent’s expert is responsible for the implementation of all
    environmental control activities at the plant
    CR. 954—56).
    He has testi-
    fied that the parent corporation,
    Borden,
    Inc., will proceed with odor
    abatement regardless of the outcome of this proceeding.(R.985).
    He
    disputes the Agency’s evidence that the odor problems emanate from the
    solvents used in the tape-making process
    (H.
    1067).
    Solvents
    with
    low
    odor
    thresholds,
    toluene,
    xylene
    and
    ethanol
    are
    to
    be
    replaced completel~
    by
    June
    of
    1973
    (.R.
    1090)
    —7—
    6
    509

    Respondent introduced testimony that incineration can achieve
    a measureable improvement
    in the odor problem
    (R.
    1136).
    The
    necessary equipment,
    installation costs and operating expenditures
    have
    all been carefully calculated
    (R.
    1058, and following).
    All
    tapes which Respondent believes are responsible for the odor
    emissions can be run on one spreader and thereby reduce the
    necessary odor abatement equipment
    (B.
    1120)
    .
    Respondent believes
    that
    if
    all of
    those tapes were
    run on the No.
    9 spreader,
    and if
    an incinerator
    is installed on that line,
    “...it would reduce the
    strength of odors significantly below any detectible levels at
    ground levels”.
    (R.
    1120).
    The Respondent’s odor emissions have violated Section
    9
    Ca)
    of the Act.
    While Respondent
    has
    conscientiously pursued various
    methods of alleviating the problem there is
    no question that the
    emissions have created a burden on the community and have
    resulted in air Dollution.
    We
    will direct Respondent to submit
    a program to alleviate this condition.
    This procedure has proven
    most effective in abating odors and has
    bCCfl
    ordered in similar
    cases.
    See Environmental Protection Agency v.
    Teepak,
    Inc.,
    ~72-8l
    (November 8,
    1972)
    3
    PCB and Environmental Protection Agency
    v. Union Carbide Corporation,
    ~72-54
    (OcLober
    3,
    1972)
    5 PCB
    We
    order Respondent
    to submit to the Board and the Agency within
    45 days,
    a plan for odor abatement at the Northfield facility.
    The
    program shall result in the complete abatement of the odor nuisance
    as soon as possible and in no case later than June 1,
    1973.
    We
    note that many odor control techniques exist of which the Respondent
    has mentioned process modification and incineration
    as having
    a high
    probability of success.
    Since process modification
    is being
    explored by Respondent
    as a means of reducing photoreactive
    hydrocarbon emissions,
    it should be possible to achieve both odor
    and hydrocarbon emission control by
    this date.
    This order, however,
    does not hold the Respondent
    to
    a particular method ;~orreducing
    odors and all possibilities should be explored in order to achieve
    the desired goal.
    We find that Respondent,
    by
    its installation and operation
    of
    No.
    9 spreader without a permit, violated Sec.
    9(b)
    of the
    Environmental Protection Act and Rule 3-2.110 of the Air Pollution
    Control Regulations.
    We
    find that Respondent’s installation of
    the odor counteractant devices without a permit, being equipment
    designed to prevent air pollution, violated Section 9~b)and Rule
    3-2.110 of the Air Pollution Control Regulations.
    A
    penalty in the
    amount
    of
    $3,500
    is
    imposed
    for
    violations
    of the statute and Rules above set forth.
    As we stated in
    Environmental Protection Agency v.
    George E. Hoffman & Sons,
    Inc.,
    ~7l-300
    (December 12,
    1972)
    6 PCB
    :“It is only by the permit
    process that the proper location and operation of a plant of this
    character can be determined and adequate equipment be installed to
    achieve compliance with the law.”
    —8—
    6—510

    Compliance
    with
    the
    requested
    procedures
    would
    have
    gone
    far
    in
    the
    elimination
    of
    odors
    and
    nuisance
    found
    to
    have
    resulted
    without
    the
    need
    for
    the
    institution of this proceeding.
    This
    opinion
    constitutes
    the findings of fact and conclusions of
    law
    of
    the
    Board.
    IT
    IS
    THE
    ORDER
    of
    the
    Pollution
    Control
    Board:
    1.
    Respondent,
    Nystik
    Tape,
    a
    Division
    of
    Borden,
    Inc.,
    is
    found
    to
    be
    in
    violation
    of
    Sections
    9(a)
    and
    9(b)
    of
    the Act and Rule
    3-2.110
    of
    the
    Air
    Pollution
    Control
    Regulations.
    Penalty in the amount of $3,500
    is assessed
    against
    Mystik
    Tape
    and
    Borden,
    Inc.
    for
    the
    aforesaid
    violation.
    Payments
    shall be made by February
    21,
    1973,
    by check or money order to Fiscal Services Division,
    Environmental
    Protection
    Agency,
    2200
    Churchill
    Drive,
    Springfield,
    Illinois 62706.
    2.
    Within 45 days from the date hereof, Mystik Tape and
    Borden,
    Inc.
    shall
    submit
    to
    the
    Board
    and
    Agency,
    a
    pro-
    gram for the abatement of air pollution and nuisance caused
    by its facility as demonstrated by the record in this pro-
    ceeding.
    The program shall result in the complete abatement
    of the odor nuisance as soon as possible and in no case later
    than June 1,
    1973.
    The Agency shall evaluate the program
    so submitted and submit its report thereon to the Board
    within
    :is days after receipt thereof.
    The Board retains
    jurisdiction of this cause for such other and further orders
    as may be appropriate.
    3.
    Respondent shall post with the Environmental Protection
    Agency, within
    60 days from the date of this Order,
    a bond
    or other security in the amount of $100,000,
    in form satis-
    factory to the Agency, which shall secure installation and
    operation of all facilities and abatement equipment to be
    installed and operated by Respondent pursuant to the program
    and installation schedules required to be submitted pursuant
    to paragraph
    2 of this Order.The bond shall be mailed to:
    Fiscal Services Division, Environmental Protection Agency,
    2200 Churchill Drive,
    Springfield, Illinois 62706.
    I, Christan Moffett, Clerk of the Illinois Pollution Control Boaçd,
    certify that the above Opinion and Order was adopted on the
    /CL,~’1
    day of
    ~
    ,
    1973,
    by
    a
    vote
    of
    .3
    to
    ,
    ~
    —9—
    6—511

    S
    S

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