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    SEP
    22009
    September 23,
    2009
    srirE.0F
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    Marie E. Tipsord
    Hearing Officer
    cThQ,V
    Illinois Pollution
    Control
    Board
    100
    West Randolph Suite
    11-500
    Chicago, Illinois
    60601
    Re:
    R2008-009,
    In The Matter of: Water
    Quality
    Standards
    and Effluent
    Limitations
    for
    the
    Chicago Area Waterway
    System and the
    Lower Des
    Plaines River: Proposed
    Amendments
    to
    35
    III. Adm.
    Code 301,
    302, 303 and 304
    Dear
    Madam Hearing Officer,
    This letter
    serves as ENVIRON’s
    response
    on
    behalf
    of Stepan
    Company to Board Member
    Dr.
    Shundar
    Lin’s
    question
    at the August 13
    hearing regarding the
    dosage of chlorine
    necessary
    to
    meet the proposed
    effluent bacteria standards
    at
    end of pipe.
    The dosage
    of
    chlorine
    determined
    by ENVIRON was 70
    mg Cl
    2!L of wastewater.
    In addition
    to providing
    the exact
    chlorine
    dose, the
    following
    comments summarize
    ENVIRON’s
    general approach
    to chlorine
    disinfection.
    First, the
    concept
    of chlorine consumption
    must be
    considered. In typical
    wastewater,
    there
    are
    four sources
    of chlorine or
    hypochlorite consumption,
    three of
    which compete with
    chlorine
    availability
    for disinfection.
    Consequently,
    adequate chlorine
    must be
    added
    to satisfy these
    sources
    of chlorine
    consumption and provide
    sufficient residual
    chlorine to
    kill fecal coliform.
    These sources
    are:
    1.
    Ammonia-N,
    which reacts
    with chlorine to form
    nitrogen
    gas;
    2. Oxidizable
    organics,
    such
    as phenols, which
    are converted to simpler
    organic
    constituents and, hopefully,
    not converted into
    chiorinated—organics;
    3.
    Oxidizable
    inorganics,
    such as cyanides, or
    sulfides, which are
    reduced
    to
    lower state compounds;
    and,
    4.
    Biological organisms,
    including fecal coliforms,
    which
    are killed in the
    presence of sufficient
    residual chlorine.
    Upon
    that
    foundation, the calculation
    of the chlorine
    dose was arrived
    in the following
    manner.
    Stepan’s
    wastewater averages
    about 2.1 mg/L
    of
    ammonia-N,
    which is a chlorine
    consumer,
    and
    it can range
    as high as 3.0 mg/L
    of ammonia-N. This will
    result
    in “breakpoint
    chlorination”
    to convert
    the
    ammonia
    to
    harmless nitrogen gas,
    requiring
    about
    15:1 Cl2 to N (See
    Design
    Manual
    Municipal Wastewater
    Disinfection.
    Cincinnati: US
    EPA Office of
    Research and
    Development,
    1986.
    Print).
    The theoretical
    dosage of chlorine
    to convert ammonia
    to nitrogen
    gas is
    47.25 mg/L
    [2.1 x 15 x
    1.5 (roughly ratio
    of maximum to average
    ammonia-N
    concentration)].
    This
    leaves approximately
    20 mg of CI2
    !L
    of
    wastewater
    for disinfection.
    From
    the
    Design of Municipal
    Wastewater Treatment
    Plants, WEF
    Manual of Practice
    No.
    8 / ASCE
    Manual
    and Report on
    Engineering Practice
    No. 76. Alexandria,
    VA: Water
    Environment
    Federation,
    1991.
    Print, Chapter 14,
    Table 14.1: Typical
    Chlorine Dosages,
    the required
    dosage
    of chlorine
    for disinfecting
    municipal
    activated sludge
    effluent can
    be up to 9
    mg!L.
    Because
    of
    201
    Summit View Drive, Suite 300,
    Brentwood, TN 37027
    www.environcorp.com
    Tel: +1
    615.377.4775
    Fax: +1 615.377.4976

    Marie
    E Tipsord
    -2-
    September
    23,
    2009
    the
    industrial
    nature of
    the Stepan wastewater,
    there will
    most
    likely be constituents
    that exert
    an
    additional chlorine
    demand (residual
    organics surfactants
    etc)
    Because
    this
    additional
    chlorine
    demand
    has not been
    quantified, a 100%
    safety factor
    was applied, rounding
    the
    required
    dosage of chlorine
    for disinfection
    to
    20
    mgIL. Adding
    that amount
    of chlorine to
    the
    amount necessary
    to address the presence
    of ammonia-N,
    which
    consumes chlorine,
    and
    rounding off the
    calculations, we
    arrived
    at 70 mg of CI
    2
    IL
    of wastewater
    to achieve
    disinfection.
    This
    dosage of
    chlorine is also what
    was implicitly reflected
    in our cost
    calculations,
    as the
    following calculations
    demonstrate:
    Design
    Flow = 1,100,000
    gal/day
    The gallons of bleach
    solution projected
    for disinfection
    = 235,883
    gal/yr (see
    Table
    8
    of Exhibit
    321), which is roughly
    646 gallons/day
    [235,883/365].
    The
    bleach
    solution is 12.5% bleach
    (NaOCI),
    so
    the bleach/liter
    of wastewater
    is
    approximately
    73 mg of NaOCl/L
    of wastewater
    [646 gals/day
    x 12.5%
    NaOCl/1,100,646
    (gallons
    of wastewater plus bleach
    solution
    in a day)].
    Using the molecular
    weights
    of sodium (Na), oxygen
    (0) and
    chlorine (Cl), the 73
    mg
    of NaOCl/L of wastewater
    is equivalent
    to 51 mg of 0C17
    L
    of wastewater
    and
    to 70 mg of Cl
    2
    /L
    of wastewater.
    Consequently,
    the dosage
    of approximately
    70 mg of
    Cl
    2
    /L
    of wastewater
    accounts for
    the
    presence of ammonia,
    susceptible organics/inorganics,
    and
    a safe residual
    for
    disinfection
    and
    served
    as the
    basis
    for our
    cost
    estimate.
    Sincerely,
    ENVIRON
    International Corporation
    Carl E.
    Adams Jr., PhD,
    PE
    Principal

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