ILLINOIS POLLUTION CONTROL BOARD
    May 19,
    1994
    IN THE MATTER OF:
    )
    )
    PETITION OF THE CITY OF EAST
    )
    AS 91—9
    MOLINE
    AND
    THE ILLINOIS ENVIRON-
    )
    (Adjusted Standard)
    MENTAL
    PROTECTION AGENCY FOR
    )
    ADJUSTED
    STANDARD FROM 35 ILLINOIS
    )
    ADMINISTRATIVE CODE 304
    )
    LEE
    R.
    CUNNINGHAM,
    of
    GARDNER,
    CARTON
    &
    DOUGLAS,
    APPEARED
    ON
    BEHALF
    OF
    THE
    CITY
    OF
    EAST
    MOLINE;
    BRUCE
    L.
    CARLSON
    APPEARED
    ON
    BEHALF
    OF
    THE
    ILLINOIS
    ENVIRONMENTAL
    PROTECTION AGENCY.
    OPINION
    AND
    ORDER OF THE BOARD
    (by R.C.
    Flemal):
    This matter comes before the Board upon a petition for
    adjusted standard filed jointly by the City of East Moline (East
    Moline) and the Illinois Environmental Protection Agency
    (Agency).
    The joint petitioners request an adjusted standard
    from the Board effluent regulations at 35 Ill. Adm. Code 304 as
    applied to the wastewater discharges from East Moline’s water
    treatment plant.
    The petition is brought pursuant to the special
    provisions regarding discharge of solids
    to the Mississippi or
    Ohio Rivers found at Section 28.3 of the Environmental Protection
    Act
    (Act)
    (415 ILCS 5/ 1 et seq.).
    The Board’s responsibility in this matter arises from the
    Act.
    The Board is charged therein to “determine, define and
    implement the environmental control standards applicable in the
    State of Illinois”
    (415 ILCS 5/5(b)) and to “grant
    ~
    an
    adjusted standard for persons who can justify such an adjustment”
    (415 ILCS 5/28.1(a)).
    More generally, the Board’s responsibility
    in this matter is based on the system of checks and balances
    integral to Illinois environmental governance: the Board is
    charged with the rulemaking and principal adjudicatory functions,
    and the Agency is responsible for carrying out the principal
    administrative duties.
    Based upon the record before it and upon review of the
    factors involved in the consideration of adjusted standards,
    the
    Board finds that East Noline has demonstrated that grant of an
    adjusted standard in the instant matter is warranted.
    The
    adjusted standard accordingly will be granted.

    —2—
    PROCEDURAL
    HISTORY
    The instant petition was filed on December 27,
    1991.
    Pursuant to 415 ILCS 5/28.3(d) (4) the cutoff date for filing
    Section 28.3 petitions was January 1,
    1992.
    The instant petition
    accordingly was timely filed.
    Hearing, which is mandatory in a Section 28.3 proceeding
    (415 ILCS 5/28.3(e), was originally scheduled for March 10,
    1992.
    However, by letter dated February 27,
    19921 the Fish and Wildlife
    Service of the U.S. Department of the Interior
    (FWS)
    raised
    concerns regarding the affects that sediment from the proposed
    discharge might have on the benthos of the receiving Mississippi
    River waters.
    Subsequent to meetings with the FWS, Illinois Department of
    Conservation, Illinois Natural History Survey, and the Office of
    the Attorney General of Illinois (Amended Petition at p.
    1), East
    Moline embarked on a series of surveys and studies intended to
    address the concerns regarding benthic organisms, with particular
    focus on mussels.
    On December 29,
    1993 joint petitioners filed an amended
    joint petition.
    The amended petition updates and supplements the
    original petition, principally as regards the mussel studies.
    The amended petition also revises the requested relief in light
    of the mussel studies.
    Hearing was held in East Moline on March 25,
    1994 before
    Hearing Officer Allen E.
    Shoenberger.
    No members of the general
    public attended the hearing.
    (Tr. at p.
    17.)
    No briefs have been filed.
    STATUTORY AND REGULATORY FRAMEWORK
    Section 28.3 of the Act, which was signed into law on
    September 7,
    1990,
    establishes provisions whereby certain
    petitioners may request of the Board an adjustment of the
    standards otherwise applicable to direct discharge of waste
    solids to the Mississippi or Ohio Rivers.
    Among particulars of
    these provisions are that the primary petitioner must be a public
    water supply2, that the raw water source be either the
    Mississippi or Ohio River, that the solids consist of clarifier
    sludge and filter backwash generated in the water purification
    1
    The letter was not received and docketed by the Board until
    March 19, 1992.
    2
    Section 28.3(b) provides that the water supply may be joined
    by the Agency as joint petitioner, as is the case here.

    —3—
    process, and that the purification process not utilize lime
    softening.
    The particular standards from which the petitioners seek an
    adjustment are the Board’s effluent standards relating to five—
    day biochemical oxygen demand
    (BOD5)
    found at 35 Ill. Adm. Code
    304.120 and to copper,
    iron, manganese,
    and total dissolved
    solids
    (TSS)
    found at 35
    Ill. Adm. Code 304.124.
    The proposed
    adjustment to these standards is that the standards not apply to
    the discharge in question provided that East Moline comply with a
    series of fourteen conditions (see following) proposed by the
    joint petitioners.
    East Moline is not seeking an adjustment of any water
    aualitv standards.
    All water quality standards would remain
    applicable to the receiving water body,
    and East Moline would,
    through the operation of
    35 Ill. Code 304.105, continue to be
    prohibited from causing or allowing the violation of all water
    quality standards.
    The joint petitioners apparently believe all
    quality standards can be met3 even though the effluent standards
    would be modified as the result of the adjusted standard.
    In determining whether an adjusted standard is to be granted
    under Section 28.3, the Board is to base its decision “upon water
    quality effects,
    actual and potential stream uses, and economic
    considerations,
    including those of the discharger and those
    affected by the discharge”.
    (415 ILCS 5/28.3(a).)
    Moreover, the
    Board is to “take into account the factors contained in
    subsection
    (a)
    of Section 27 of the Act”
    (415 ILCS 5/28.3(f)).
    These factors include “the existing physical conditions,
    the
    character of surrounding land uses,
    zoning classifications, the
    nature of the
    .
    .
    .
    receiving body of water,
    .
    .
    .
    and the
    technical feasibility and economic reasonableness of measuring or
    reducing the particular type of pollution”.
    (415 ILCS 5/27(a).)
    The roles assigned to the Agency in the Section 28.3 process
    include that of proposal reviewer and, where the Agency so deems,
    joint petitioner.
    The Agency has compiled a guidance document
    specifying its conditions of review
    (See Petition Attachment A).
    ~ Joint petitioners allow that attainment of compliance
    might entail invoking allowed mixing, pursuant to 35 Ill. Adm.
    Code 302.102, and perhaps the necessity of defining a mixing zone
    as part of East Moline’s NPDES permit.
    (Petition,
    p.
    4.)
    Joint
    petitioners indicate that they do not anticipate problem with
    East Moline obtaining a mixing zone or a zone of inital dilution.
    (u.)

    —4—
    DISCUSSION
    Current Operations/Existing Physical Conditions
    East Moline operates a water treatment plant located at 901
    12th Avenue in East Moline.
    (Petition at p.
    14.)
    The plant
    provides clarified,
    filtered, disinfected water to approximately
    6,500 residences
    (22,000 people) and approximately 100 businesses
    in East Moline.
    (~.
    at p.
    15.)
    The plant has a capacity of
    10
    million gallons per day, but the average pumping rate is 4.0 MGD
    The raw water source for the treatment plant is the
    Mississippi River.
    The raw water is delivered to the water
    treatment plant via a pumping station located at 7th Street and
    1st Avenue in East Moline.
    (Petition at p.
    15.)
    The raw water is subject to various treatments,
    including
    the addition of powdered activated carbon for removal of taste
    and odors,
    copper sulfate to reduce algal growth,
    lime and alum
    for flocculation and pH adjustment,
    chlorine and ammonia for
    disinfection, and fluoride.
    (Petition at p.
    15,
    16.)
    Sediment is removed from the raw water at two principal
    points, within sedimentation basins and in sand filtration units.
    (Petition at
    p.
    16.)
    The discharges at issue are generated from
    these two sources,
    as a result of dragging of the sedimentation
    basins and during backwashing of the filters.
    The sediment wastestreams are currently discharged through
    two outfalls.
    Discharge from the sediment basins is through
    outfall 001; discharge from the filter backwash operations is
    through outfall 002.
    Both outfalls are on an unnamed tributary
    of the Mississippi River.
    Flow thereafter follows the unnamed
    tributary for approximately 1000 feet before entering a storm
    sewer and thence discharging into the Mississippi River.
    Currently the sediment discharges are on an intermittent
    basis.
    Cleaning of both sediment basins and filters are
    performed as needed, with filter backwashing typically occurring
    for 20 minute periods four times daily and dragging of the
    sedimentation basins typically occurring for 1½ to two hour
    periods once every 36 hours.
    (Petition at p. 8-9.)
    Character of the Mississippi River/Discharge Area
    The Mississippi River in the vicinity of East Moline is a
    multi—use waterway.
    It is a major navigational waterway.
    It is
    used for sport fishing and boating.
    In addition to East Moline,
    it is also utilized as a source of drinking water by Rock Island.
    It is also a discharge point for wastewater treatment facilities
    and for stormwater runoff from both rural and urban areas.

    —5—
    Water quality of the Mississippi River in the vicinity of
    the discharge is generally good.
    (Petition at p.
    9.)
    A
    biological survey conducted in 1987 also indicated that the
    biological integrity of the river, as measured by biological
    index, number of organisms,
    and total number of taxa found, was
    similar upstream and downstream of the existing East Moline
    outfall.
    (~.
    at p.
    10.)
    Joint petitioners contend that the
    discharge system as proposed herein would actually cause a net
    decrease in the sediment loadings to the Mississippi River, and
    accordingly should tend to improve water quality.
    (Petition at
    p.
    40.)
    Character of Surrounding Land Uses
    Joint petitioners described the surrounding land use as
    follows:
    Side stream property is predominately industrial,
    except for a small residential area around the proposed
    discharge point.
    This property is separated from the
    Mississippi River by a road and flood levee.
    Between
    the bicycle path and the river is steeply graded riprap
    which drops off approximately 18 feet to the shore,
    thereby greatly limiting access to the river from the
    adjacent property.
    (Petition at
    p.
    8.)
    Proposed Modifications and New Discharcre System
    Joint petitioners propose as a condition of the adjusted
    standard that the present discharge configuration be replaced by
    a direct discharge to the Mississippi River.
    The new direct
    discharge would take place though a 3-inch pipe extending from
    the water plant to approximately 70 feet
    (22
    in)
    beyond the shore
    of the Mississippi River.
    Moreover, as additional conditions of the adjusted standard,
    East Noline proposes to replace the intermittent discharges with
    continuous discharges.
    The filter backwash and sedimentation
    basin discharges would be directed to a mixing tank that has a
    continuous discharge of approximately 100 gallons per minute.
    Joint petitioners declare that “this will avoid any impact from
    intermittent loadings and reduce the area of the mixing zone,
    thereby minimizing any adverse impact on the River”
    (Petition at
    p.
    9)
    Among the principal concerns raised during the course of
    this matter has been whether the proposed sediment discharges
    would have a negative impact on benthic organisms in the
    receiving water,
    and particularly whether the discharge would
    adversely impact either mussel beds or endangered or threaten
    mussel species.
    This concern has occasioned a delay of more than
    two years in the conduct of the hearing in this proceeding
    (see

    —6—
    above) and has been the impetus for most of the issues raised in
    the amended petition.
    Both the design and location of the proposed discharge point
    have been modified as the result of the mussel studies.
    The
    design has been reconfigured to add a diffuser that would project
    the discharge upward at a 30-degree angle.
    Model studies
    indicate that this diffuser would produce a maximum increase in
    the suspended solids concentration of 22 mg/i (71:1 dilution
    ratio)
    on the river bed,
    a level that joint petitioners consider
    to have no adverse impact on mussels.
    (Amended Petition at p.
    5
    and attachment FF.)
    Initially the new discharge point was proposed to be located
    approximately 1400 feet upstream of the present storm sewer
    outfall.
    (Petition at p.
    5-6.)
    However, based on the mussel
    studies,
    joint petitioners now recommend that the discharge occur
    immediately offshore of the present storm sewer discharge.
    This
    site, known as “Dive Area #2” in the various mussel studies
    (see
    Amended Petition attachments), was selected based on the absence
    of mussels in a transect from the shore to the proposed discharge
    point
    (Amended Petition attachment LL at p.
    3.)
    and a sparse
    mussel population (absence of mussel beds)
    in the projected plume
    of the discharge
    (~.
    at p.
    4).
    At the point of proposed
    discharge the bottom of the Mississippi River is sediment.
    (~.
    at p.
    10.)
    As regards the matter of endangered or threaten mussel
    species, the Illinois Department of Conservation on February 25,
    1994 issued a biological opinion pursuant to 17
    Ill.
    Adm. Code
    1075.40(e).
    The opinion concludes
    that the discharge of water treatment solids to
    the Mississippi River by the City of East Moline is not
    likely to have significant adverse effects on
    endangered or threatened species of freshwater mussels
    that may be present in the vicinity of the discharge.
    This conclusion has been reached with understanding
    that the discharge will be installed in
    accordance
    with the conditions specified in the amended petition.
    (Co-Petitioner’s Hearing Exhibit #1 at p.
    1.)
    Net Sediment Reduction
    A singular facet of the conditions proposed by the joint
    petitioners is the provision that East Noline obtain land that is
    presently being farmed and to hold the land as fallow land.
    The
    purpose is to “more than offset the net amount of solids added to
    the Mississippi River from the discharge of its mixing tank as
    compared to the amount of solids which result from the raw water
    used”
    (Petition at p.
    29-30).
    The joint petitioners further note
    that:

    —7—
    To do so East Moline will first calculate its
    annual solids loading to the Mississippi River.
    It
    will then calculate the annual solids loading in the
    raw water and subtract that value from its annual
    loading to determine its net annual loading to the
    Mississippi.
    East Moline, with the assistance of the
    local Soil and Water Conservation District, will next
    identify available land parcels, and for each parcel it
    will calculate,
    using the Universal Soil Loss Equation,
    the annual solids loading which will be expected from
    land which is actively farmed.
    It will then subtract
    from that value the annual loading calculated from the
    same land as fallow land, thereby determining the net
    annual reduction in loading.
    Finally,
    it will obtain
    sufficient land to result in a total net annual
    reduction in solids loading to the Mississippi River of
    double its net annual loading due to discharges from
    its water plant.
    (Petition at
    p.
    30.)
    Technological and Economic Considerations
    East Moline has undertaken various efforts to maximize
    operational procedures and to minimize chemical use, so as to
    improve the quality of the discharged water and reduce the impact
    of the discharge on the river.
    (Petition at p.
    16—23.)
    Several
    of the procedures are now in place, and others, such as designing
    the discharge system to maximize diffusion and to direct the
    discharge plume away from the bed of the river,
    are proposed as
    part of the agreed—upon conditions to the grant of the instant
    adjusted standard.
    The Agency would exercise oversight of the
    conditions,
    among other matters, through the construction,
    operating,
    and NPDES permits that are required for the
    implementing the adjusted standard.
    East Moline has also investigated compliance options that
    would not require an adjusted standard.
    (Petition at p.
    26.)
    Among these, the most economical option would be to pass the
    sediment wastestreams though standard treatment operations.
    Consultants for East Moline estimate that capital cost and annual
    costs of this operation would be $581,000 and $396,000,
    respectively.
    As compared to East Moline’s proposal, which has a
    capital cost of $460,400 and annual costs of $93,000~,the most
    economical compliance option accordingly would cost an additional
    $120,000
    in capital and $197,000 per year in operating expenses.
    (Petition at p.
    37.)
    Over a twenty-year period the proposed
    ~ The Board notes that these figures are for the discharge
    configuration proposed in the original petition.
    Since the joint
    petitioners have not updated these figures, the Board assumes
    that the costs for the discharge configuration proposed in the
    amended petition do not significantly differ from those of the
    original petition.

    —8—
    adjusted standard would thus save East Moline approximately $20
    million.
    (u.)
    Joint petitioners summarize the economic considerations by
    observing:
    The economic impact upon those affected by the
    discharge is
    ...
    positive since there will be no
    impairment of actual or potential uses and many of
    those affected are customers of the water plant.
    Since
    East Moline’s proposal
    is a lower cost alternative,
    water bills will not increase as much as they would if
    East Moline were required to comply with generally
    applicable standards.
    (Petition at p.
    37.)
    CONCLUSION
    Based upon its consideration of the record presented in this
    action, the Board finds that the joint petitioners have provided
    justification necessary for an adjusted standard to be granted
    with conditions.
    This opinion constitutes the Board’s findings of fact and
    conclusions of law in this matter.
    ORDER
    The City of East Moline
    (East Moline)
    is hereby granted an
    adjusted standard applicable to the discharge of wastewater from
    a water treatment plant located at 901 12th Avenue in East
    Moline,
    Illinois, which as of the date of this order discharges
    wastewater from its sedimentation basin through outfall 001 to an
    unnamed tributary of the Mississippi River at 41°31’
    08” north
    latitude and 90°26’ 32” west longitude and wastewater from its
    filter backwash which discharges to the same tributary through
    outfall 002 at 41°31’
    09” north latitude and 90°26’
    30” west
    longitude.
    Pursuant to this adjusted standard, the effluent
    standards for BOD5,
    total suspended solids,
    iron, manganese, and
    copper set forth at 35 Ill.
    Adm. Code 304.120 and 304.124 do not
    apply to these discharges.
    This grant of adjusted standard is
    contingent upon East Moline complying with each of the following:
    1.
    Within ninety
    (90) days of this order East Moline shall
    apply for all construction and operation permits,
    including NPDES permit revisions,
    necessary to comply
    with the conditions of this adjusted standard.
    East
    Moline shall promptly provide any supplemental
    information needed for those applications,
    if any such
    information is identified by the Agency.

    —9—
    2.
    Within two years of the date of obtaining the necessary
    construction permits the water plant shall cease
    discharging to the unnamed tributary of the Mississippi
    River and shall commence discharging directly to the
    Mississippi River.
    3.
    The discharge to the Mississippi River shall be through
    a pipe which extends approximately 22 meters into the
    Mississippi River from the shore from a point near the
    present stormwater outfall to the Mississippi River
    approximately 1600 feet west of 7th street.
    4.
    Until at least January 1,
    1996,
    East Moline shall
    maintain as fallow land approximately 33.7 acres which
    are part of Farm #2116, Tax Parcel 350 and 351 in Coe
    Township and after that date shall either continue to
    maintain that land as fallow land or shall obtain,
    through lease or purchase, other agricultural land
    which at the time of acquisition is not fallow land and
    which is calculated through the use of the Universal
    Soil Loss Equation to contribute a net suspended solids
    loading to the Mississippi River
    (as compared to the
    calculated loading for fallow land)
    of least an average
    of 500 tons per year of the term of the lease or
    ownership or the water plant shall implement some other
    plan approved by the Agency for offsetting the water
    plant’s net contribution of suspended solids to the
    Mississippi River.
    5.
    Within two years of the date of obtaining the necessary
    construction permits East Moline shall construct a
    surge tank with a capacity of at least 100,000 gallons
    to hold its filter backwash wastewater prior to
    discharge.
    6.
    As much of the wastewaters from the surge tank
    described in Paragraph 5, above, as can reasonably be
    returned to the headworks of the water plant for
    retreatment, consistent with reliable and lawful
    operation of the water plant,
    shall be so returned.
    7.
    Within two years of the date of obtaining the necessary
    construction permits East Moline shall construct and
    place into operation a mixing tank of not less than
    50,000 gallons capacity to hold the wastewater from the
    water plant’s sedimentation basins prior to discharge
    to the Mississippi River.
    8.
    The wastewaters from the surge tank described in
    Paragraph 5,
    above, which are not returned to the
    headworks of the water plant pursuant to Paragraph 6,
    above,
    shall be mixed with wastewaters from the

    —10—
    sedimentation basins,
    if any, prior to discharge to the
    Mississippi River.
    9.
    Any
    overflows from the surge tank described in
    Paragraph 5,
    above, which are not handled pursuant to
    paragraphs
    6 or 8, above,
    shall be directed to East
    Noline’s wastewater treatment plant for treatment.
    10.
    All mussels found at the time of construction which
    would be anticipated to be directly impacted by the
    construction activities shall be relocated to a
    suitable area outside of the area of direct impact.
    11.
    Each year for a period of five
    (5) years after the
    commencement of the discharge East Moline shall perform
    a mussel survey to evaluate the impact of the discharge
    upon the mussels, and shall sample sediment copper
    concentrations, weather conditions reasonably
    permitting.
    12.
    Within one year after the commencement of the
    discharge,
    East Moline shall perform a study to verify
    the accuracy of the modeling conducted by Mr. James
    Huff as described in Attachment FF of the Amended Joint
    Petition, including sampling of water quality
    downstream of the discharge point for total suspended
    solids, hardness
    (as CaCO3), total copper and soluble
    copper to verify the effectiveness of the high velocity
    port discharge.
    13.
    The activities required by Conditions 10 through 12,
    above,
    shall be carried out in accordance with the
    Scope-of-Work set forth at Attachment JJ of the Joint
    Amended Petition in this matter regarding the
    performance of various mussel surveys before and after
    the commencement of the water plant’s discharge to the
    Mississippi River, the verification of field conditions
    after operation begins, and sampling for copper and
    hardness.
    14.
    The granting of this adjusted standard is not to be
    construed as affecting the enforceability of any
    provisions of this adjusted standard, other Board
    regulations, the Act, the Clean Water Act,
    or any
    federal regulation.
    Section 41 of the Environmental Protection Act (415 ILCS
    5/41
    (1992)) provides for the appeal of final Board orders within
    35 days of the date of service of this order.
    The Rules of the
    Supreme Court of Illinois establish filing requirements.
    (See
    also 35 Ill.Adm.Code 101.246 “Motions for Reconsideration”.)

    —11—
    IT IS SO ORDERED.
    I, Dorothy N. Gunn, Clerk of the Illinois Pollution Control
    Board, hereby Certi~ythat the above opinion and order was
    adopted on the
    /‘~‘—
    day
    of
    avoteof
    __________
    1994, by
    I
    Control Board

    Back to top