ILLINOIS POLLUTION CONTROL BOARD
    May
    9,
    1986
    IN THE MATTER OF:
    )
    )
    THE JOINT PETITION OF THE CITY
    )
    OF ROCK ISLAND AND THE ILLINOIS
    )
    PCB 85-214
    ENVIRONMENTAL PROTECTION AGENCY
    )
    FOR EXCEPTION TO THE COMBINED
    )
    SEWER OVERFLOW REGULATIONS
    )
    MR. ROY HARSCH APPEARED ON BEHALF OF THE CITY OF ROCK ISLAND
    MR. THOMAS DAVIS APPEARED ON BEHALF OF THE ENVIRONMENTAL
    PROTECTION AGENCY
    OPINION AND ORDER OF THE BOARD (by R.
    C. Flemal):
    This matter comes before the Board upon a joint petition for
    a combined sewer overflow
    (CSO)
    exception filed pursuant to 35
    Ill.
    Adm.
    Code,
    Subtitle
    C,
    Chapter
    I,
    Part 306,
    Subpart
    D, by
    the City of Rock Island (“Rock Island”) and the Illinois
    Environmental Protection Agency (“Agency”).
    Petitioners
    specifically request exception from 35
    Ill. Adm.
    Code 306.305(a)
    and 306.305(b).
    The Board conducted
    a public hearing
    in Rock Island on March
    3,
    1986.
    In addition to testimony presented by the Joint
    Petitioners,
    testimony
    in support of the requested relief was
    presented by Ms. Emily
    Smith, chairperson of the Rock Island
    Facilities Study Jury of Experts.
    The Jury of Experts consists
    of thirteen citizens, representing
    a cross-section of community
    interests,
    who have followed the progress of all phases of the
    CSO program for several years.
    CSO
    •REGULATI~NS
    The CSO regulations are contained
    in
    35
    Ill. Adm.
    Code,
    Subtitle
    C, Chapter
    I,
    Part 306.
    They were amended in R81-17,
    51
    PCB 383, March 24,
    1983.
    Section 306.305 provides
    as follows:
    All combined sewer overflows and treatment plant
    bypasses shall be given sufficient treatment to prevent
    pollution,
    or the violation of applicable
    water
    standards unless an exception has been granted by the
    Board pursuant to Subpart
    D.
    69-425

    -2-
    Sufficient treatment shall consist of the following:
    a)
    All dry weather flows, and the first flush of storm
    flows as determined by the Agency,
    shall meet the
    applicable effluent standards; and
    b)
    Additional
    flows,
    as determined by the Agency but
    not less than ten times to average dry weather flow
    for the design year, shall receive
    a minimum of
    primary treatment and disinfection with adequate
    retention time;
    and
    c)
    Flows
    in excess of those described in subsection
    (b)
    shall be treated,
    in whole or
    in part,
    to the extent
    necessary to prevent accumulations
    of sludge
    deposits, floating debris and solids
    in accordance
    with
    35
    Ill. Adm.
    Code 302.203,
    and
    to prevent
    depression of oxygen levels; or
    d)
    Compliance with
    a treatment program authorized by
    the Board
    in an exception granted pursuant to
    Subpart
    D.
    Subpart
    D allows the discharger to file
    a petition for an
    exception either singly, or jointly with the Agency,
    as Rock
    Island has done.
    A joint petition may seek an exception based on
    minimal discharge impact
    as prov~idedin Section 306.361(a):
    An exception justification based upon minimal discharge
    impact shall include,
    as
    a minimum, an evaluation of
    receiving stream ratios,
    known stream uses,
    accessibility to stream and side land use activities
    (residential, commercial,
    agricultural, industrial,
    recreational),
    frequency and extent of overflow events,
    inspections of unnatural bottom deposits, odors,
    unnatural floating material or color,
    stream morphology
    and results of limited stream chemical analyses.
    Rock Island and the Agency believe they have made the “minimal
    impact” showing pursuant to Section 3O6.361(a).
    SUPPORT DOCUMENTS
    Rock Island has undertaken several studies of its CSO
    situation,
    the reports of which have been submitted as exhibits
    in support of the petition.
    The principal among these is the
    R~ckI~sl~and.,
    i1I.inois
    Combined
    Sew-er-
    Overflo-w
    .St-udy,
    prepared
    by
    Missman,
    Stanley
    & Associates, dated May,
    1982,
    and
    submitted
    as
    Exhibit
    2 (referenced
    as Exhibit
    B in Joint
    Petition).
    This
    document
    is augmented by two other
    Missrnan,
    Stanley
    & Associates
    studies,
    a response supplement
    to the IEPA review letter dated
    August,
    1983 (Ex.
    1; referenced
    as Exhibit
    A in Joint Petition),
    69-426

    —3—
    and Propos-ed•Pla-n-for-POTW-a-ndTra-nsport-Iii~prove~ent-s•-for-•3oin-t
    CSO -Exception dated
    September, 1984
    (Ex.
    5;
    referenced as Exhibit
    E in Joint
    Petition).
    These studies consider, among other
    matters, description of the Rock
    Island sewage transport and
    treatment system, characterization of alternate control
    mechanisms,
    determination of the quantity and quality of CSOs,and
    assessment
    of the impact of the overflows on the Mississippi
    River.
    A fourth major document submitted as Exhibit
    3
    (referenced
    as
    Exhibit
    C
    in Joint Petition)
    was prepared by James
    E.
    Huff,
    P.E., and deals with CSO effects on stream bottom sediments.
    The
    record before the Board also contains several exhibits submitted
    in support of particular aspects of the testimony presented at
    hearing.
    BACKGROUND
    The City of Rock Island, which has
    a population of 46,862
    (1980 census),
    is located in northwestern Illinois on the
    Mississippi and Rock Rivers.
    Rock Island owns and operates its
    own system of sewers
    and waste treatment plants.
    The system
    includes approximately 170 miles of sewers.
    It also includes
    two-
    treatment plants,
    the Main Plain and the Southwest Plant.
    Only
    the Main Plant and its tributary sewer system are the subject of
    the joint petition.
    The Main Plant
    is
    served by two major
    interceptor
    sewers,
    the North Slope Interceptor and the South
    Slope Interceptor.
    As with many older cities
    in the Midwest, Rock Island
    originally constructed combined sewers to convey both municipal
    sewage and stormwater.
    Between 1970 and 1979 Rock Island
    undertook
    a $6.9 million program to separate combined sewers
    serving about 2,830 acres of the 5,600 acres
    tributary to the
    Main Plant
    (R.
    at
    10).
    At present approximately 17
    of the area
    tributary to the Main Plant
    (970 of 5,600 acres)
    remains
    combined.
    The combined areas are located
    in the north-central
    section of the city
    (Ex.
    10),
    and correspond with the principal
    commercial areas of the community (Ex,
    2, Table
    1)
    where
    separation would be most difficult and expensive
    (R. at 11).
    The requested exception concerns six outfall structures:
    outfall OO1A is
    a bypass located at the Main Treatment Plant;
    outfalls 002-006 are overflows
    from the North
    Slope
    Interceptor.
    Outfall OO1A discharges directly to the Mississippi
    River.
    Outfalls 002-006 discharge in the lower reaches of Sylvan
    Slough,
    a high-velocity side channel of the Mississippi River
    which has been developed as
    a race-way for
    a hydroelectric plant
    located upstream from the CSO discharges
    (R.
    at
    59).
    69-427

    —4—
    The Main Treatment Plant consists of two parallel grit
    removal chambers, eight primary settling tanks,
    the complete mix
    activated sludge process, two secondary clarifiers,
    and
    chlorination facilities.
    The plant has an
    8 million gallons per
    day
    (“mgd”) design average flow capacity and a
    16
    rngd maximum
    flow capacity.
    The North Slope
    Interceptor is
    a ninety-six
    inch
    sewer with
    a full pipe capacity of 204 mgd.
    As conditions associated with granting of the requested
    exception, Rock Island agrees to undertake certain modifications
    to its system.
    These involve the construction of head works
    improvements to allow operation of the treatment plant at the
    design maximum level of 16 uigd and improvements to the North
    Slope Interceptor to assure that maximum available transport
    capacity will be utilized prior to overflow events.
    The
    modifications consist of
    (1) improvements to the screening system
    at an estimated installation cost of $75,000,
    (2) interceptor
    chamber modifications at an estimated cost of
    $23,000,
    and
    (3)
    increase in elevations of diversion weirs
    at an estimated cost of
    $3,000,
    The agreed to improvements thus aggregate to
    a total
    estimated cost of $101,000.
    The improvements are further
    detailed
    in Exhibit
    5.
    DOCUMENT-ATION- OF MINIMAL -IMPACT
    The Mississippi River in the reach of the CSO and the bypass
    outfalls has recreational use for boating and fishing (R. at 22);
    small boating use
    is characterized as
    “heavy”
    (R.
    at 28).
    Some
    water skiing does occur, but the amount of swimming which occurs
    is not addressed
    in the record
    (R.
    at 29).
    The river, but not
    Sylvan
    Slough,
    is also used for commercial barge traffic.
    The
    nearest downstream known withdrawal of water for public water
    supply is at Muscatine,
    Iowa,
    approximately 25 miles downstream.
    Access
    to the river in the vicinity of the CSOs and bypass
    is limited.
    Through most of the reach
    in question the community
    is separated from the river by a levee which does not have any
    point of public access
    (R.
    at
    21).
    Land between the levee and
    the river
    is variously barren sand flats, rock flats, and/or
    woods which range
    in width up to 150 yards, depending in part on
    river stage
    (R.
    at 21-8).
    Additionally, much of the landward
    side of the levee
    is occupied by industrial land of limited
    access.
    From March to August of 1980, an overflow monitoring and
    sampling program was conducted to collect basic data on the
    quantity and quality of the CSO overflows.
    This program
    consisted of measuring flow at the six discharge points with
    continuous flow meters, monitoring of the length of time the Main
    Plant pumps directed discharge to outfall OO1A,
    sampling of water
    quality,
    and physical inspection of the five CSO discharge
    points.
    69-428

    —5-
    Data from the 1980 monitoring and sampling program was
    utilized, along with historical rainfall data,
    to estimate the
    number and volumes of overflow events that could be expected
    in
    an average year;
    the estimation was done utilizing the computer
    program,
    Simplified
    Storm Water Management Model (SSWMM).
    This
    analysis indicates the following number and volumes of events
    from each discharge point per year
    (Ex.
    11):
    NUMBER
    VOLUME
    OUTFALL
    OF- -EVENTS
    ~-mg/y-ea-r•)
    OO1A
    103
    697.2
    002
    16
    12.5
    003
    24
    7.6
    004
    50
    10.3
    005
    40
    79.3
    006
    50
    9.6
    These data indicate that bypass OO1A can be expected to discharge
    approximately 700 million gallons from 103 events during the
    average year.
    Similarly,
    the five other
    CSOs can be expected to
    discharge approximately 120 million gallons during approximately
    50 events per year
    (R.
    at 36-7).
    The
    120 million gallon figure
    would be reduced by 20
    and the number of events decreased to 40
    per year
    if the improvements as agreed to by Petitioners are
    implemented
    (R. at 43).
    Not all of the 700 million gallons discharged at OO1A is
    derived from the combined sewer system.
    Due to the particular
    configuration of the Main Plant
    (Ex.
    19),
    some separated storm
    sewer discharges are directed through outfall OO1A (Ex.
    19).
    It
    is estimated that about 1/3 of the 700 million gallons derives
    from separated storm
    sewers
    (R.
    at
    73).
    Similarly,
    some of the 103 annual events estimated for
    outfall OO1A are apparently triggered by infiltration into the
    separated storm sewer system rather than by storm surcharging of
    the combined sewer system
    (R. at
    55,
    61-71).
    The pumps at OO1A
    are afixed to wet wells which receive flow from both the storm
    and sanitary sewer system
    (Ex.
    19).
    The filling of these wet
    wells causes the pumps
    to activate and drain the wells via the
    outfall.
    The record
    is unclear as to what percentage of the 103
    events are related to simple emptying of the wet wells.
    At one
    point
    it
    is
    surmised
    that
    infiltration
    is responsible for causing
    the wells
    to fill and discharge approximately
    20 to 30 times per
    year
    (R.
    at 49-50).
    Later in the record
    it
    is indicated that
    these could constitute
    “the majority” of the pumping events at
    OO1A
    (R.
    at
    61), and that they constitute approximately half of
    the 103 events
    (R.
    at
    76).
    Petitioners have presented testimony
    that during 1985 there were only seven occurrences of bypasses at
    OO1A which were occasioned by flow to the Main Plant exceeding
    the plant’s
    16 mgd design maximum flow
    (R. at 105).
    69-429

    —6—
    In comparing the volumes of the
    CSOs to the flow
    in the
    receiving stream, Petitioners note that the mean daily discharge
    of the Mississippi River at Rock Island
    is 31,085 mgd, and that
    the ten-year seven-day low flow is 8,900 mgd
    (Petition,
    par.
    12).
    In contrast, an overflow event of
    a one-year frequency
    would discharge about 52.7 million gallons
    (Petition, par. 12).
    Thus, if the one-year recurrence interval discharge were to occur
    at the time of average flow in the Mississippi,
    it would be
    subject
    to
    a receiving ratio
    of 590:1; if it occurred
    at the time
    of the ten-year seven-day low flow it would be subject to a
    mixing ratio of 169:1.
    Chemical analyses of the CSO discharges
    as conducted- in
    1980
    included the following parameters: biochemical oxygen demand
    (BUD),
    chemical oxygen demand
    (COD),
    total suspended solids
    (TSS), total dissolved solids
    (TDS), ammonia nitrogen,
    phosphorous, and lead.
    Volume analysis indicated that the six
    CSOs in combination make an average annual contribution of 0.6
    million pounds
    of BOD and 4.5 million pounds of TSS to the
    Mississippi River.
    Over 80
    of these contributions are
    discharged from at the Main Plant via OO1A due to the larger
    volume, number of events,
    and pollutant loadings
    at that point
    (R.
    at
    37).
    Given the high flows of the Mississippi River,
    Petitioners conclude that
    “the Rock Island CSOs by themselves
    have
    a negligible effect on the Mississippi River water quality”
    (Petition,
    par.
    12; Ex.
    2,
    p.
    176).
    In
    a more recent study (Huff Study,
    Ex.
    3), assessment was
    made of the impact of Main Plant outfall OO1A*
    on bottom
    sediments.
    The assessment was undertaken through independent
    sampling of the bottom sediments and by analysis of previous
    sampling data collected by the Agency in July 1984,
    and by
    Missman, Stanley & Associates
    in May,
    1985.
    All samples were
    subjected to chemical analysis as well as physically inspected.
    Samples were analyzed for lead,
    zinc,
    oil and grease, volatile
    solids, and total solids.
    In addition, the samples were ranked
    blind
    by
    three
    individuals
    for
    odor
    intensity.
    The
    Huff
    Study
    found
    that
    discharges
    from
    the
    bypass
    CSO
    has
    resulted
    in a limited area along the near shore of the river with
    elevated pollutant levels.
    This area
    is approximately five
    hundred feet in length by fifty
    feet in width.
    To provide
    perspective to the levels of pollutants
    as found,
    Huff compared
    the observed levels to those recorded in
    a general Agency study
    of bottom sediments collected from sites downstream of sewage
    treatment plants
    (Ex.
    16).
    In the case of CSO OO1A all mean
    values of observed constitutents are below the mean values found
    ‘There
    is no sedimentation below the five North Slope Interceptor
    CSOs, where the river bottom consists of solid rock.
    69-430

    —7—
    by the Agency
    in the general survey of sediment collected within
    one mile of wastewater treatment plant outfalls.
    On this basis,
    Huff concludes that the “impact from the existing Rock Island
    combined sewer overflows on the Mississippi River
    is not
    discernible based upon these sediment results
    in the zone of
    impact”
    (R.
    at
    84).
    To further assure that the CSOs have minimal environmental
    impact,
    Rock Island has agreed,
    as
    a condition to granting of the
    exception,
    to implement
    a one-year shoreline inspection
    program.
    This program
    is intended to quantify and document
    the
    amount of debris attributable to the CSOs
    (R.
    at.
    16).
    ECONOMIC -HARDSHIP
    Rock Island has determined preliminary cost estimates for
    full compliance with
    Section 306.305(a) and 306.305(b).
    Under
    these rules Rock Island would be required to provide complete
    treatment for the first flush of storm flows.
    An additional ten
    times the average design dry weather flow would require primary
    sedimentation and disinfection.
    The Petitioners believe that
    these requirements would necessitate,
    as the least expensive
    option,
    the provision of below ground,
    covered, off-line storage
    -
    facilities to capture and reduce the occurrence of overflows or
    plant bypasses.
    These storage facilities would operate
    in
    integration with the main treatment plant, and would allow for
    total capture and subsequent secondary treatment of the first
    flush.
    Additionally, full compliance would require upgrading the
    Main Plant to allow attainment of current design standards for
    treatment plant components and hydraulic capacity (Petition,
    par.
    4).
    In aggregate the full compliance alternative was estimated
    in 1982 to cost $25.2 million, and the annual operation and
    maintenance costs were estimated
    to be $3.7 million (Ex.
    2,
    p.
    181).
    Later figures,
    as set forth in Exhibits
    1 and
    12, raise
    these figures
    to a total of $54.9 million in capital costs and
    $6.9 million in operating costs under the assumption that total
    suspended solids control would also be required.
    The latter
    amounts would be
    “slightly lower
    if treatment based upon
    biological
    (sic) oxygen demand
    (BUD)
    was required”
    (Petition,
    par. 4).
    At hearing Mr. Robert
    T. Hawes,
    City Engineer of Rock
    Island,
    further testified that the cost of full compliance is
    estimated to be $54,330,000, and if these costs were spread over
    a
    20 year period at
    an interest rate of 8,
    the average
    residential sewer use charge would increase from $3 charge would
    increase from S37.21 to $103.90 per quarter.
    69-431

    —8-
    DISCUSSION -OF- ORDER
    The
    Board
    determines that Petitioners
    have
    shown
    pursuant
    to
    35
    Ill.
    Adm.
    Code
    3O6,361(a)
    that exception to
    35
    Ill.
    Adm.
    Code
    306.305(a),
    as
    it relates to first
    flush of storm flows, and to
    35 Ill.
    Adrn.
    Code
    306.305(b)
    would
    produce
    minimal
    impact
    on
    the
    receiving stream.
    Accordingly, the Board will grant the
    exception.
    The Board further will accept the conditions
    as
    agreed to by Petitioners.
    The Board notes that the Agency has emphasized that its
    support of this petition is predicated on the assumption that the
    relief is restricted only to those substantive requirements for
    effluent treatment of CSOs, and not to relief from water quality
    standards
    (R.
    at 94).
    Rock Island appears to have been aware of
    this condition, and has not objected
    to it.
    The Board itself
    notes that up to the present time, the United States
    Environmental Protection Agency has indicated that only variance
    (i.e. non-permanent) relief from water quality
    standards can be
    granted consistent with the Clean Water Act (see document
    entitled “Status Report on Discussions with USEPA”,
    dated October
    4,
    1985;
    this document
    is part of the record of, and is cited in,
    Bor-den--Chemic•al-Gompa-ny--v-~-Illinois--Env-ir-onment-al -Protect-ion
    ~enc•y, PCB 82-82,
    PCB
    ,
    December
    5,
    1985).
    To assure
    that this issue is clear,
    the Board will introduce into the
    Order,
    as proposed by Petitioners, language identifying the scope
    of the exception
    as granted.
    ORDER
    1.
    The City of Rock Island is hereby granted an exception
    from the treatment requirements of
    35
    Ill.
    Adm.
    Code 306.305(a),
    as such provision relates to first flush of storm flows, and from
    35 Iii. Adm.
    Code 306.305(b),
    subject to the following
    conditions:
    a.
    Such
    exception
    shall
    be
    limited
    to
    combined
    sewer
    outfalls 002, 003,
    004,
    005,
    and
    006
    and to bypass
    OO1A,
    as
    identified in this proceeding.
    b.
    The City of Rock Island shall implement all
    modifications to its sewer system as identified
    in
    paragraphs 14,
    15, and
    16 of the petition in this
    proceeding.
    c.
    The City of Rock Island shall implement the
    shoreline inspection program described
    in paragrpah
    15 of the petition in this proceeding.
    2.
    This grant
    of exception does not preclude the Agency
    from exercising its authority to require as
    a permit condition a)
    a
    CSO monitoring program sufficient to assess compliance with
    69-432

    -9—
    this exception and any other
    Board regulations, including Section
    306.305(c); and b) other controls
    if needed for compliance,
    including compliance with water quality standards.
    3.
    This grant of exception is not to be construed as
    affecting the enforceability of any provisions of this exception,
    other Board regulations, or the Act.
    4.
    Within forty-five days of the date of this Order, the
    City shall execute
    a Certification of Acceptance and Agreement to
    be bound
    to all terms and conditions of the exception granted.
    The Certification shall be submitted to the Agency at 2200
    Churchill Road, Springfield,
    Illinois,
    62706.
    The forty-five day
    period shall
    be held
    in abeyance during any period that this
    matter is being appealed.
    The form of said Certification shall
    be as follows:
    CERTIFICATION
    I,
    (We),
    ___________________________,
    having read the
    Order of the Illinois Pollution Control Board,
    in PCB 85-214,
    dated May
    9, 1986, understand and accept the said Order,
    realizing that such acceptance renders all terms and conditions
    thereto binding and enforceable.
    Petitioner
    By:
    Authorized Agent
    Title
    Date
    IT IS SO ORDERED.
    Board Members Joan Anderson and Jacob
    D. Dumelle concurred.
    I, Dorothy
    M. Gunn,
    Clerk of the Illinois Pollution Control
    Board, hereby certify that the above Opinion and Order was
    adopted on the
    _______
    -~7-cZ.
    day
    of
    -)7a~-~
    ,
    1986,
    by
    a vote of
    -
    -
    -~‘7--.~
    ~Z-fl-~
    Dorothy
    M. G~znn, Clerk
    Illinois
    Pollution Control Board
    69-433

    Back to top