BEFORE
    THE
    ILLINOIS
    POLLUTION
    CONTROL
    BVE
    CLERK’S
    OFFICE
    V.
    ILLINOIS
    ENVIRONMENTAL
    PROTECTIONAGENCY,
    Respondent.
    PCB
    09-025
    JAN
    02
    2009
    STATE
    OF
    ILJJNOIS
    olIutjon
    Control
    Board
    TO:
    See
    Attached
    Service
    List
    NOTICE
    OF
    FILING
    PLEASE
    TAKE
    NOTICE
    that
    on
    January
    2,
    2009,
    we
    filed
    with
    the
    Office
    of
    the
    Clerk
    of
    the
    Pollution
    Control
    Board
    Joliet’s
    Witnesses
    Narrative
    Testimony,
    a
    copy
    of
    which
    is
    served
    upon
    you.
    Dated:
    January
    2,
    2009
    Roy
    M.
    Harsch,
    Esq.
    Yesenia
    Villasenor-Rodriguez,
    Esq.
    Drinker
    Biddle
    &
    Reath
    LLP
    191
    North
    Wacker
    Drive
    -
    Suite
    3700
    Chicago,
    Illinois
    60606
    (312)
    569-1441
    (Direct
    Dial)
    (312)
    569-3441
    (Facsimile)
    CITY
    OF
    JOLIET,
    Petitioner,
    )
    )
    )
    )
    )
    )
    )
    )
    )
    )
    (Permit
    Appeal-Water)
    THIS
    FILING
    IS
    BEING
    SUBMITTED
    ON
    RECYCLED
    PAPER

    BEFORE
    THE ILLINOIS
    POLLUTION CONTROL
    BOARD
    LERK’S
    OFFICE
    CITY
    OF
    JOLIET,
    )
    JAN
    02
    Petitioner,
    )
    ILLINOIS
    v.
    )
    PCB
    09-025
    )
    (Permit Appeal-Water)
    ILLINOIS
    ENVIRONMENTAL
    )
    PROTECTION
    AGENCY,
    )
    )
    Respondent.
    )
    JOLIET’S
    WITNESSES
    NARRATIVE
    TESTIMONY
    The
    CITY
    OF
    JOLIET
    (hereinafter,
    “Joliet”),
    by
    its
    attorneys,
    Drinker
    Biddle
    &
    Reath
    LLP, pursuant
    to
    35
    Ill.
    Adm.
    Code Section
    10
    1.626(d)
    and
    in
    accordance
    with
    the
    Hearing
    Officer’s
    directive
    submits
    the
    following
    pre-hearing
    written
    testimony
    for
    the
    following
    witnesses.
    These
    witnesses
    will
    be
    present
    at
    the
    hearing
    and
    will
    be
    available
    for
    cross-
    examination.
    1.
    Harold
    Harty
    of
    the
    CityofJoliet
    (Attachment
    A)
    2.
    Dennis
    Duffield
    of
    Rogina
    &
    Associates,
    Ltd.
    (Attachment
    B)
    3.
    Eli
    Port
    (Attachment
    C)
    4.
    Richard
    Toohey
    of
    Oak
    Ridge
    Associated
    Universities
    (Attachment
    D)
    Dated:
    January
    2,
    2009
    Roy
    M.
    Harsch, Esq.
    Yesenia
    Villasenor-Rodriguez,
    Esq.
    Drinker
    Biddle
    &
    Reath
    LLP
    191
    North
    Wacker
    Drive
    -
    Suite
    3700
    Chicago,
    Illinois
    60606
    (312)
    569-1441
    (Direct
    Dial)
    (312)
    569-3441
    (Facsimile)
    THIS
    FILING
    SUBMITTED
    ON
    RECYCLED
    PAPER

    CERTIFICATE
    OF
    SERVICE
    I, the
    undersigned,
    certify
    that
    I
    have
    served
    the
    attached
    Joliet’s
    Witnesses
    Narrative
    Testimony
    by
    First
    Class
    Mail,
    postage
    pre-paid
    on
    January
    2,
    2009.
    See
    Attached
    List.
    Yes
    n
    Villasenor-Rodrigue
    THIS
    FILING
    SUBMITTED
    ON
    RECYCLED
    PAPER

    Service
    List
    PCB
    09-25
    (Permit
    Appeal
    Water)
    Gerald
    Karr
    Senior
    Assistant
    Attorney
    General
    69
    West
    Washington
    Suite
    1800
    Chicago,
    IL
    60602
    John
    T.
    Therriault
    Illinois
    Pollution
    Control
    Board
    James
    R.
    Thompson
    Center
    100W.
    Randolph
    Street—
    Suite
    11-500
    Chicago,
    IL
    60601
    Bradley
    P.
    Halloran
    HearingOfficer
    Illinois
    Pollution
    Control
    Board
    James
    R.
    Thompson
    Center
    100
    W.
    Randolph
    Street
    Suite
    11-500
    Chicago,
    IL
    60601
    CHO1/25278359.1
    THIS
    FILING
    SUBMITTED
    ON
    RECYCLED
    PAPER

    WRITTEN
    TESTIMONY
    OF
    HAROLD
    HARTY
    IN
    THE
    MATTER
    OF
    City
    of
    Joliet
    v.
    Illinois
    EPA
    PCB 09-25
    Before
    the
    Illinois
    Pollution
    Control
    Board
    Bolingbrook,
    Illinois
    January
    13,
    2009
    My name
    is
    Harold
    Harty.
    My business
    address
    is
    1021
    McKinley,
    Joliet,
    Illinois.
    I
    have
    been employed
    by
    the
    City of
    Joliet for
    the
    past 34
    years.
    In
    the
    last
    28
    years,
    I have
    been
    the
    Plant
    Operations
    Superintendent
    in
    charge
    of
    three
    (3)
    wastewater
    treatment
    plants.
    I
    hold an
    Illinois
    Class
    1 Wastewater
    Treatment
    Plant
    Operator’s
    License
    and
    an
    Illinois
    Class
    B
    Water
    Treatment
    Plant
    Operator’s
    License.
    In
    1982,
    the
    City
    of
    Joliet
    started
    the
    Land
    Application
    Program
    for
    the
    disposal
    of
    bio
    solids
    from
    the
    wastewater
    treatment
    plants.
    We felt
    at
    that
    the
    time
    that
    recycling
    bio
    solids
    to
    be
    used
    as
    fertilizer
    was the
    best
    use
    for
    this
    material. Our
    bio-solids
    program
    has
    been
    in
    operation
    since
    then
    and
    has
    met
    or
    exceeded
    all
    requirements
    set
    by
    the
    Illinois
    Environmental
    Protection
    Agency
    (“IEPA”)
    and
    the
    United
    States
    Environmental
    Protection
    Agency
    (“U.S.
    EPA”)
    standards.
    We started
    this
    program
    to
    assure
    proper
    disposal,
    and
    have
    closely
    followed
    all
    of
    the
    applicable
    environmental
    requirements.
    As
    a
    result,
    Joliet has
    never
    received
    a
    warning
    letter
    or
    any
    other
    complaint
    regarding
    its
    sludge
    disposal
    operations.
    From
    the
    start
    of
    the
    program
    we
    recognized
    that
    Joliet
    would
    need
    a
    knowledgeable
    City
    representative
    to
    interact
    with
    those
    whose
    land would
    be
    used.
    We
    needed
    someone
    that
    had
    an
    established
    relationship
    with
    landowners/growers.
    Joliet
    understood
    that
    we
    would
    needed
    to
    gain acceptance
    of
    the
    program.
    Joliet
    therefore
    decided
    to
    contract
    with
    a
    trained
    Agronomist
    to
    meet
    these
    needs.
    From
    the
    start,
    our
    Agronomist
    recorded
    the
    application
    rates
    and monitored
    loadings
    for
    each
    field
    that
    received
    Joliet’s
    bio-solids.
    During
    the
    early
    years,
    the
    number
    of
    allowable
    applications
    were
    limited
    by
    copper
    and
    zinc
    loads
    due
    to
    their
    concentration
    in
    the
    bio—solids.
    With
    the
    continuing
    proper
    implementation
    of
    pre-treatment,
    bio-solids
    applications
    are
    now
    controlled
    by
    nitrogen
    and
    phosphorus.
    From
    the
    start of
    this
    program,
    Joliet
    used
    an
    independent
    Agronomist
    to
    do
    all
    of
    the
    field-testing
    required
    by
    the
    permit
    we
    received
    from
    the
    IEPA
    which
    authorized
    the
    land
    application
    of
    our
    bio-solids.
    This
    contractor
    set
    the
    agronomical
    rates
    to
    accommodate
    to
    the
    field
    conditions
    and
    to
    ensure
    that
    the
    proper
    amounts
    of
    bio-solids
    are
    applied
    to
    the
    fields.
    Exhibit
    is
    a
    statement
    from
    our
    current
    Agronomist,
    Mr.
    Daniel
    Fiedler
    of Land
    Treatment
    Alternatives,
    Inc.,
    which
    provides
    some
    additional
    information
    regarding
    our
    bio-solids
    disposal
    program
    which
    he
    oversees.
    I

    Our
    bio-solids
    are
    generated
    in
    our
    treatment
    plants
    from
    the
    treatment
    of
    sanitary
    sewage.
    Sludge
    settles
    in
    plant
    clarifiers
    and
    is
    directed
    to
    digesters
    at
    each
    plant.
    Bacteria
    in
    the
    digesters
    reduce
    the
    amount
    of
    organic
    matter
    and
    stabilize
    the
    sludge
    for
    land
    application.
    The
    bio-solids
    are
    collected
    in
    the
    anaerobic
    digesters
    at
    our
    two
    older
    plants
    and
    in
    the
    aerobic
    digester
    at
    our
    newer
    Aux
    Sable
    plant.
    The
    bio-solids
    are
    transferred
    to
    storage
    tanks
    at
    each
    plant
    site.
    Our
    bio-solids
    program
    uses
    an
    annual
    agreement
    with
    each
    landowner/grower
    whose
    fields
    have
    been
    identified
    by
    our
    Agronomist
    as
    potential
    fields
    for
    the
    contract
    period.
    The
    Agronomist
    identifies
    the
    specific
    field
    for
    application
    and
    establishes
    the
    rate
    of
    application.
    All
    farmers
    are
    informed
    of
    what
    is
    in
    our
    bio-solids
    and
    sign
    a
    User
    Information
    Sheet
    form
    accepting
    the
    bio-solids.
    The
    landowner/grower
    must
    sign
    this
    form
    that
    identifies
    the
    analysis
    of
    the
    sludge
    and
    the
    crop
    to
    be
    grown
    and
    the
    yield
    goal.
    The
    hauling
    and
    land
    application
    is
    contracted
    by
    public
    bid
    to
    licensed
    applicators
    who
    are
    independent
    of
    the
    Agronomist.
    The
    Applicator
    provides
    tank
    trucks
    to
    transport
    liquid
    sludge
    from
    plants
    to
    each
    specific
    field
    in
    the
    program.
    Each
    truck
    holds
    approximately
    5500
    gallons
    per
    load.
    The
    Applicator
    provides
    fertilizer
    applicators
    with
    chisel
    plows
    mounted
    with
    ihjectors
    to
    apply
    the
    biosolids
    below
    the
    ground
    surface
    in
    the
    top
    12
    inches
    of
    soil.
    The
    application
    rates
    established
    by
    the
    Agronomist
    and
    agreed
    to
    in
    writing
    by
    the
    landowner/grower
    are
    utilized.
    The
    percentage
    of
    solids
    of
    the
    sludge
    applied
    and
    the
    gallons
    applied
    are
    recorded
    to
    verify
    application
    rates.
    The
    Agronomist
    adds
    the
    current
    application
    to
    the
    records
    of
    the
    total
    applied
    to
    a
    given
    field.
    Total
    loadings
    are
    compared
    to
    U.S.
    EPA
    and
    IEPA
    allowed
    loadings
    to
    assure
    compliance.
    This
    program
    has
    grown
    throughout
    the
    years
    to
    where
    we
    are
    applying
    bio-solids
    to
    about
    1,000
    acres/year.
    There
    has
    always
    been
    more
    demand
    for
    the
    bio-solids
    then
    we
    have
    ever
    produced.
    Farmers
    know
    the
    value
    of
    our
    product
    to
    their
    operation
    as
    an
    alternative
    to
    commercial
    fertilizer,
    which
    has
    steadily
    increased
    over
    the
    years.
    Although
    the
    growers
    recognize
    the
    fertilizer
    value,
    they
    also
    recognize
    the
    additional
    compaction
    of
    the
    soil
    in
    the
    field
    which
    potentially
    reduces
    yield.
    To
    encourage
    acceptance
    of
    sludge
    in
    the
    spring,
    growers
    are
    paid
    $50
    per
    acre
    for
    the
    right
    to
    apply
    the
    bio-solids
    and
    up
    to
    an
    additional
    $50
    per
    acre
    is
    paid
    if
    the
    crop
    yield
    is
    less
    than
    the
    five
    year
    average
    yield
    for
    that
    field.
    Wet
    soil
    in
    the
    spring
    leads
    to
    more
    compaction
    than
    a
    mid-summer
    application
    on
    a
    dry
    field.
    The
    City
    of
    Joliet’s
    Land
    Application
    Program
    has
    become
    a
    model
    for
    others
    to
    follow.
    This
    program
    has
    merit
    in
    that
    we
    are
    recycling
    this
    product
    to
    the
    best
    use
    of
    technology.
    The
    only
    alternative
    would
    be
    to
    landfill,
    which
    has
    no
    benefit
    to
    the
    environment.
    This
    program
    and
    the
    City
    of
    Joliet
    have
    always
    completed
    everything
    the
    IEPA
    has
    regulated
    and
    will
    continue
    to
    do
    it
    in
    the
    future.

    The
    continuation
    of
    the
    land
    application
    program
    will
    allow
    an
    on-going
    recycling
    effort
    and
    keep
    this
    material
    out
    of
    the
    landfill.
    In
    order
    to
    landfill
    this
    sludge,
    it
    would
    have
    to
    be dried,
    requiring
    the
    construction
    of
    specific
    drying
    facilities
    and tipping
    fees
    would
    have
    to
    be
    paid.
    These
    additional
    costs
    will
    be
    covered
    in
    the
    narrative
    testimony
    of
    Mr.
    Dennis
    Duffield.
    The
    first
    time
    that
    we
    received
    a
    permit
    from
    IEPA
    that
    contained
    a
    limitation
    on
    Radium
    was
    in
    permit
    2006-SC-4784
    issued
    in
    October
    2006.
    We
    were
    immediately
    concerned
    because
    it
    only allowed
    for
    a
    total
    accumulative
    increase
    of
    radium
    to
    exceed
    a
    level
    of
    0.1
    pico
    curies
    per
    gram
    from
    the
    application
    of
    sludge.
    We
    were
    told
    by
    our
    Agronomist
    and
    consultants
    that the
    number
    of
    applications
    would
    be
    limited
    to
    only
    one
    application.
    With this
    severe
    limitation,
    our Agronomist
    felt
    that
    it
    would
    be
    very
    difficult,
    if
    not
    impossible,
    to
    get
    landowners/growers
    to
    agree
    to
    be
    part
    of
    our
    program.
    They
    simply
    would
    not
    want
    to
    be
    bothered
    with
    the
    program
    and
    the
    potential
    interference
    with
    their
    farming
    operations
    for such
    limited
    benefit.
    Accordingly,
    we
    began
    a
    series
    of
    discussions
    with
    the
    JEPA
    to
    attempt
    to
    reach
    agreement
    to
    raise
    the
    permitted
    level.
    (Record
    at
    R-6
    through
    R-96).
    These efforts
    will
    be described
    in
    greater
    detail
    by
    Mr.
    Duffield.
    In
    summary,
    while
    we
    were
    able
    to
    get
    JEPA
    to
    issue
    permit
    2006-SC-4784-2
    which
    raised
    allowable
    the
    total
    accumulative
    increase
    limit
    to
    0.4
    pico
    curies
    per
    gram,
    we
    were
    still
    concerned
    because
    this
    level
    still
    would
    limit
    the
    number
    of
    applications
    to
    four
    from
    the
    higher
    rate
    that
    is
    currently
    only
    being
    limited
    by
    the
    nutrient
    loadings
    of
    the
    bio-solids.
    This
    would
    eventually
    mean
    that
    more
    and
    more
    land
    would
    be
    needed
    to
    be
    identified
    by
    our
    Agronomist
    and
    signed
    up
    to
    be
    part
    of
    the
    program.
    This
    would
    also
    mean
    that
    the distances
    to
    these
    fields
    from
    our
    three
    plants
    would
    increase.
    This
    would
    result
    in
    increased
    hauling
    costs
    and greater
    emissions
    from
    the
    trucks.
    While
    we
    were
    grateful
    that
    IEPA
    agreed
    to
    increase
    the
    Radium
    level
    to
    0.4
    pico
    curies
    per
    gram
    because
    it
    allowed
    our
    Agronomist
    to
    continue
    to
    work
    with
    existing
    landowners/growers
    to
    gain additional
    applications,
    such
    a
    value
    still
    limited
    the
    total
    number
    of
    applications.
    Our
    consultants
    and
    experts
    continued
    to
    say
    that
    there
    was
    no
    real
    need
    for
    this
    low
    of
    a
    limit.
    Therefore,
    Joliet continued
    to
    have
    discussions
    with
    IEPA;
    and,
    we
    agreed
    to
    request
    a
    formal
    modification
    to
    our
    permit
    to
    change
    the
    limit
    to
    1.0
    pico
    curies
    per
    gram
    and
    supply
    all
    of
    the
    supporting
    information
    our
    consultants
    and
    experts
    had
    developed
    to
    support
    the request.
    A
    permit
    modification
    was
    filed
    which
    was
    received
    by
    IEPA
    on
    July
    30,
    2008.(Record
    at
    R-1)
    By
    letter
    dated
    September
    12,
    2008,
    the
    IEPA
    denied
    the
    permit
    modification
    request.(Record
    at
    R-1
    through
    R-2)
    Joliet
    filed
    the
    present
    appeal
    on
    October
    17,
    2008.
    We
    are
    here
    today,
    to
    challenge
    the
    IEPA
    decision
    and
    we
    will
    show
    through
    the
    testimony
    of
    our consultants
    and
    experts
    that
    the
    decision
    is
    without
    merit
    and
    should
    be
    reversed
    by the
    Illinois
    Pollution
    Control
    Board.
    CHO1/
    25275549.2

    WRITTEN
    TESTIMONY
    OF
    DENNIS
    L.
    DIJFFIELD
    IN
    THE
    MATTER
    OF
    City
    of
    Joliet
    v.
    Illinois
    EPA
    PCB
    09-25
    Before
    the
    Illinois
    Pollution
    Control
    Board
    Bolingbrook,
    Illinois
    January
    13,
    2009
    My
    name is
    Dennis
    L.
    Duffield.
    My
    business
    address
    is
    93
    Caterpillar
    Drive,
    Joliet
    IL,
    60436.
    I
    was
    granted
    a
    Bachelor’s
    of
    Science
    in
    Civil
    Engineering
    by
    Bradley
    University
    in
    Peoria,
    IL
    in
    1972
    I
    am
    currently
    employed
    as
    Project
    Manager
    for
    Rogina
    and
    Associates,
    Ltd.
    Prior
    to
    my
    employment
    at
    Rogina
    and
    Associates,
    I
    was
    employed
    by
    the
    City
    of
    Joliet
    for
    26
    years;
    For
    all
    but
    the
    first
    four
    months
    of
    employment
    with
    the
    .City
    of
    Joliet,
    I was
    responsible
    for
    the
    planning,
    design,
    construction
    and
    operations
    of
    the
    municipal
    water
    and
    wastewater
    systems.
    I
    served
    as
    the
    Director
    of
    Public
    Works
    and
    Utilities
    for
    25
    years.
    During
    this
    time,
    Joliet
    was
    required
    to
    address
    the
    issues
    concerning
    radium
    in
    drinking
    water,
    a
    new
    radium
    water
    quality
    standard
    and
    overly
    restrictive
    limitations
    on
    the
    disposal
    of
    biosolids
    (wastewater
    treatment
    plant
    residuals)
    containing
    radium.
    I
    believe
    that
    it
    is
    important
    that
    the
    Illinois
    Pollution
    Control
    Board
    (“Board”)
    understand
    the
    history
    and background
    of
    radium
    regulations
    in
    order
    to
    be
    able
    to
    properly
    assess
    and
    decide
    the
    issue
    presented
    in
    this
    appeal.
    Accordingly,
    I will
    first
    present
    a
    review
    of
    the
    regulatory
    process
    and
    the
    impact
    it
    had
    on
    Joliet’s
    sludge
    disposal
    program.
    I
    am
    hopeful
    that
    this
    will
    allow
    the
    Board
    to
    understand
    the
    impact
    that
    this
    appeal will
    have
    on
    Joliet and
    ultimately
    the
    regulated
    community
    here
    in
    Illinois.
    Radium
    Regulation
    The 1976
    Safe Drinking
    Water
    Act
    and
    the
    public
    water
    supply
    regulations
    that
    the
    United
    States
    Environmental
    Protection
    Agency
    (“U.S. EPA”)
    adopted
    pursuant
    thereto
    created
    a maximum
    contaminant
    level
    for
    combined
    radium
    226
    and
    radium
    228.
    This
    level was
    5.0
    pico-curies
    per
    liter.
    Upon
    the
    implementation
    of
    this
    maximum
    contaminant
    level,
    the Public
    Water
    Supply
    Division
    of
    the
    Illinois
    Environmental
    Protection
    Agency
    (“IEPA”)
    arranged
    for
    the
    analysis
    of
    water
    from
    drinking
    water
    systems
    in
    Illinois.
    Joliet
    was
    included
    in
    this initial
    sampling.
    However
    due
    to
    numerous
    delays
    in
    the
    analysis
    of
    the
    samples,
    Joliet
    was
    not
    notified
    of
    an
    exceedence
    of
    this
    standard
    until
    1985.
    1

    IEPAIIDNS
    Memorandum
    of
    Agreement
    Without
    providing
    any
    advance
    notice
    to
    those
    entities
    that
    operate
    either
    water
    supplies
    or
    wastewater
    treatment
    plants
    and
    without
    providing
    any
    ability
    to
    comment,
    the
    ]EPA
    and
    the
    Illinois
    Department
    of
    Nuclear
    Safety
    entered
    into
    a
    Memorandum
    of
    Agreement
    (Record
    at
    R-336
    through
    R-339)
    in
    1984
    which
    set
    forth
    the
    responsibilities
    of
    both
    agencies
    with
    respect
    to
    the
    disposal
    and
    use
    of
    sludge
    resulting
    from
    the
    treatment
    of
    water
    or
    sewage
    containing
    naturally
    occurring
    radium
    from
    ground
    water.
    This
    agreement
    limited
    the
    land
    application
    of
    bio-solids
    containing
    radium
    to
    assure
    that
    the
    increase
    in
    soil
    concentration
    be
    limited
    to
    0.1
    pico-curies
    per
    gram.
    The
    majority
    of
    my
    testimony
    addresses
    IEPA’s
    first
    stated
    basis
    for
    the
    denial
    of
    Joliet’s
    requested
    permit
    modification
    which
    is
    this
    Memorandum
    of
    Agreement
    Notice
    of
    Drinking
    Water
    Violation
    Joliet
    received
    notice
    from
    the
    IEPA
    in
    1985
    that
    the
    JolietPublic
    Water
    Supply
    must
    be
    brought
    into
    compliance
    with
    the
    Safe
    Drinking
    Water
    Act’s
    maximum
    contaminant
    level
    for
    combined
    radium
    226
    and
    radium
    228.
    Joliet’s
    Actions
    After
    conducting
    a
    study,
    it
    was
    determined
    that
    the
    best
    solution
    for
    Joliet
    was
    to
    construct
    a
    new
    water
    supply
    using
    the
    Kankakee
    River
    as
    a
    source.
    The
    land
    acquisition
    necessary
    for
    the
    newwater
    supply
    and
    thepreparation
    of
    plans
    and
    specifications
    were
    proceeding
    until
    1991.
    On
    July
    18,
    1991,
    the
    United
    States
    Environmental
    Protection
    Agency
    (“U.S.
    EPA”)
    formally
    proposed
    a
    new
    maximum
    contaminant
    level
    for
    radium.
    This
    proposal
    allowed
    a
    concentration
    of
    20
    pico-curies
    per
    liter
    of
    radium
    226
    and
    20
    pico-curies
    per
    liter
    of
    radium
    228.
    If
    this
    proposal
    was
    approved
    by
    U.S.
    EPA,
    Joliet
    would
    have
    come
    into
    compliance
    without
    any
    new
    construction.
    Joliet,
    as
    did
    many
    other
    communities
    in
    Northern
    Illinois
    which
    used
    the
    same
    deep
    well
    aquifers,
    stopped
    work
    on
    the
    Kankakee
    River
    Project
    pending
    a
    decision
    on
    the
    new
    proposal.
    Stakeholder’s
    Meeting
    For
    years
    following
    the
    initial
    proposal,
    there
    was
    very
    limited
    public
    activity
    by
    the
    U.S.
    EPA
    on
    the
    radium
    proposal
    until
    a
    Stakeholder’s
    Meeting
    was
    scheduled
    and
    held
    on
    December
    11
    -
    12,
    1997
    at
    the
    Hyatt
    Regency
    Crystal
    City
    2799
    Jefferson
    Davis
    Highway
    Arlington,
    VA
    22202.
    There
    is
    a
    record
    of
    the
    meeting
    at
    htlp
    ://www.epa.
    gov/safewater/ndwac/sumradn.html.
    2

    I attended the
    meeting
    on
    behalf
    of
    Joliet.
    Also
    present
    at the
    meeting
    from
    Illinois
    were
    Gerald
    Bevers
    of
    the
    City
    of DeKaib
    and
    Roger
    Selburg,
    Manager,
    Division
    of
    Public
    Water
    Supplies,
    LEPA.
    One
    of
    the
    topics
    of
    discussion
    at
    the
    meeting
    was
    the
    generation
    of
    radium
    water
    treatment
    residuals
    and
    their
    disposal.
    Sanitary
    sewers
    were
    listed
    by
    U.S.
    EPA
    as
    an
    acceptable alternative
    for
    disposing
    of
    water
    treatment
    plant
    residuals.
    In discussions
    at
    that
    time
    with
    Roger
    Selburg,
    I
    was
    advised
    that
    the
    radium
    residuals
    could
    be
    discharged
    to
    the
    sanitary
    sewer
    as the
    radium
    was
    already
    being
    discharged
    to
    the
    sanitary sewer
    prior
    to
    treatment.
    Radium
    was
    pumped
    from
    the
    deep
    wells,
    into
    user’s homes
    and
    then
    discharged
    to
    the
    sanitary
    sewer.
    With
    the
    implementation
    of
    radium
    treatment
    to
    meet
    drinking
    water
    regulations,
    radium
    would
    be
    pumped
    from
    the
    deep
    wells,
    then
    treated
    to
    provide
    homeowners
    with
    water
    meeting
    standard
    and
    that
    water
    discharged
    to
    the
    sanitary sewer.
    The
    radium
    removed
    by
    the
    water
    supply
    treatment
    could
    also
    be
    discharged
    to
    thc
    sanitary
    sewer.
    The
    total
    amount
    of
    radium
    pumped from
    the
    deep
    wells
    would
    reach
    the
    wastewater
    treatment
    plant
    unchanged
    using
    either
    approach.
    Notice
    of
    Data
    Availability,
    Proposed
    Rule
    On
    April
    21,
    2000,
    the
    U.S.
    EPA
    published
    a
    Notice
    of
    Data
    Availability
    and
    Proposed
    Rule
    for
    Radium
    that
    took
    me,
    and
    many
    in
    both
    the
    regulatory
    and
    regulated
    community,
    by
    complete surprise.
    U.S.
    EPA
    proposed
    that
    combined
    radium
    226
    and
    228
    should
    not
    exceed
    5.0
    pico-curies
    per
    liter.
    This
    was
    almost
    identical
    to
    the
    original
    1976
    rule.
    Final
    Rulemaking
    After
    receiving
    comments
    from
    the
    public,
    U.S.
    EPA
    issued
    a final
    rule
    on
    December
    7,
    2000.
    This
    rule
    was
    scheduled
    to
    become
    effective
    on
    December
    8,
    2003.
    It was
    essentially
    the
    same rule
    that
    had
    been
    proposed
    earlier
    in
    2000.
    This
    rule
    essentially
    left
    in
    place
    the
    requirement
    of
    combined
    radium
    226
    and
    radium
    228
    to
    be
    below
    5.0
    pico
    curies
    per
    liter.
    Joliet’s Response
    to
    Rulemaking
    Joliet
    had
    grown
    greatly
    since
    1985
    and
    the
    original
    intake
    and
    treatment
    plant
    was
    no
    longer properly
    sized
    to
    meet
    Joliet’s
    growing
    demand.
    A new
    intake
    site
    on
    the
    Kankakee
    River
    was
    selected
    and
    work
    began
    with
    the
    Illinois
    Department
    of
    Natural
    Resources,
    Division
    of
    Water Resources
    to
    obtain
    a
    withdrawal
    permit
    at
    the
    new
    site.
    Soon thereafter
    based
    on
    the
    anticipated
    difficulty
    in
    obtaining
    a withdrawal
    permit
    from
    the
    Kankakee
    River,
    Joliet
    elected
    to
    perform
    an
    additional
    study
    to
    determine
    what
    would
    be
    the
    best
    source
    and
    treatment
    for
    Joliet.
    3

    A
    team
    of
    three
    consulting
    engineers
    and
    Joliet
    staff
    was
    assembled
    to
    review
    the
    new
    technologies
    available
    for
    radium
    removal,
    proven
    technologies
    and
    a
    Kankakee
    River
    based
    supply.
    Contact
    was
    made
    with
    the
    Illinois
    State Water
    Survey
    to
    determine
    the
    continued
    availability
    of
    water
    from
    the
    deep
    sandstone
    aquifer.
    The
    results
    of
    this
    study
    were
    as
    follows:
    1.
    Water
    from
    the
    deep
    aquifer
    will
    be
    available
    for
    25
    to
    100
    years
    according
    to
    information
    provide
    by
    the
    Illinois
    State Water
    Survey.
    Joliet
    interpreted
    this
    information
    as
    a
    reason
    to
    invest
    in
    additional
    deep
    wells
    instead
    of
    the
    Kankakee
    River
    Project.
    2.
    The
    selected
    treatment
    technique
    was
    Co-precipitation
    of
    Radium
    with
    Hydrous
    Manganese
    Oxide.
    This
    report
    was
    completed
    in
    August
    of
    2003.
    Joliet
    proceeded
    immediately
    to
    select
    a
    consulting
    engineer
    and
    pilot
    testing
    of
    the
    hydrous
    manganese
    treatment.
    IEPA
    Actions
    Faced
    with
    a
    growing
    amount
    of
    knowledge
    concerning
    the
    discharge
    of
    waste
    water
    from
    communities
    using
    deep
    well
    aquifers
    containing
    natural
    radium,
    the
    IEPA
    filed
    a
    radium
    water
    quality
    standard
    rulemaking
    on
    January
    13,
    2004.
    This
    rulemaking
    was
    accepted
    by
    the
    Board
    and
    docketed
    as
    R2004-02
    1.
    The
    IEPA
    proposed
    that
    the
    water
    quality standard
    for
    radium
    be
    eliminated
    in
    the
    general
    use
    standards
    and
    that
    a
    water
    quality standard
    of
    5.0
    pico-curies
    per
    liter
    upstream
    of
    a food
    processing
    plant
    intake
    or
    public
    water
    supply
    intake
    be
    established.
    As
    a
    review
    of
    the
    record
    from
    this
    proceeding
    will
    show,
    I
    was
    actively
    involved
    through
    out
    this
    rulemaking
    proceeding.
    This
    rule making
    started
    on
    January
    13,
    2004
    and
    was
    completed
    on
    March
    15,
    2006.
    The
    rule
    that
    was
    finally
    adopted
    by
    the
    Board
    in
    this
    proceeding
    varied
    greatly
    from
    the
    IEPA
    proposed
    and
    included
    the
    following
    water
    quality
    standards:
    1.
    GENERAL
    USE
    WATER
    QUALITY
    STANDARDS
    The
    annual
    average
    radium
    226
    and 228
    (STORET
    number
    11503)
    combined
    concentration
    must
    not
    exceed
    3.75
    pico-curies
    per
    liter
    (pCi/L).
    2.
    PUBLIC
    AND
    FOOD
    PROCESSING
    WATER
    SUPPLY
    STANDARDS
    Radium
    226
    and
    228
    (STORET
    number
    11503)
    combined
    concentration
    must
    not
    exceed
    5
    pico-curies
    per
    liter
    (pCi/L)
    at
    any
    time.
    4

    Information
    from
    the
    Rulemaking
    Process
    During
    the
    course
    of
    the
    hearings
    concerning
    the
    proposed
    rule,
    Joliet
    first
    became
    aware
    of
    the
    1984
    Memorandum
    of
    Agreement
    between
    the
    TEPA
    and
    the
    Illinois
    Department
    of
    Nuclear
    Safety
    concerning
    land
    application
    of
    residuals:
    I
    immediately
    recognized
    the
    potential
    impact
    that
    this
    twenty year
    old
    document
    could
    have
    and
    begun
    to
    try
    to
    sort
    out
    an
    approach
    that
    Joliet
    could
    follow
    and
    an
    approach that
    the
    TEPA
    could
    support.
    After
    talking
    about
    the
    potential
    impact
    of
    the
    Memorandum
    of
    Agreement
    with
    various
    JEPA
    personnel,
    I prepared
    a
    letter
    to
    Jeff
    Hutton
    dated
    April
    9,
    2004
    providing
    an
    analysis
    of
    land
    application
    of
    wastewater
    treatment
    plant
    residuals
    containing
    radium
    (Record
    at
    R-294
    through
    R-304).
    I sent
    the letter
    to
    Jeff
    Hutton
    because
    he
    was
    the
    focal
    point for
    sludge
    regulation
    and
    penrlitting
    at
    the
    IEPA.
    As
    stated
    in
    the
    letter,
    I
    was
    concerned
    that
    the
    impact
    of
    land application
    had
    not
    been
    considered
    although
    communities
    were
    committing
    to
    water
    treatment
    techniques
    to
    comply
    with
    the
    combined
    radium
    226
    and
    radium
    228
    to
    be
    below
    5.0
    pico-curies
    per
    liter
    drinking
    water
    standard
    that
    resulted
    in
    residuals
    being
    discharged
    to
    the
    wastewater
    treatment
    plant
    IEMA-DNS
    Response
    JEPA
    forwarded
    Jbliet’s
    April
    2004
    letter
    to
    the
    Illinois
    Emergency
    Management
    Agency,
    Division
    of
    Nuclear
    Safety
    (“IEMA-DNS”)
    for
    review
    and
    comment.
    Due
    to
    a
    re-organization
    of
    state government,
    the
    nuclear
    safety
    function
    had
    been
    placed
    under
    the
    Illinois
    Emergency
    Management
    Agency.
    IEMA-DNS
    sent
    JEPA
    their
    review
    of
    the
    Joliet request
    in
    a
    letter
    dated
    May
    10,
    2004
    to
    Al
    Keller.
    (Record
    at
    R
    292-293)
    The
    comments
    received
    from
    IEMA-DNS
    were
    directed
    at
    Joliet’
    request
    to
    make
    five
    applications
    of
    biosolids
    to
    a
    given
    field.
    IEMA-DNS
    viewed
    this
    as
    “unrestricted
    land
    application
    of
    radium
    contaminated
    sewage
    sludge”
    that
    would
    create
    sites
    requiring
    land
    use
    restrictions.
    The
    other
    major item
    in
    the
    IEMA-DNS
    comments
    was
    that
    DNS
    thought
    that
    Joliet
    may
    be
    in
    violation
    of
    the
    Memorandum
    of
    Understanding
    by
    land
    applying
    sludge
    that
    increased
    the
    soil
    radium
    concentration
    by
    greater than
    0.1
    pico-curies
    per
    gram.
    Joliet’s
    Response
    to
    the
    IEMA-DNS
    comments
    First
    it
    is
    not
    possible
    for
    Joliet
    to
    violate
    the
    Memorandum
    of
    Agreement
    as
    this
    document
    in
    not
    an
    enforceable
    rule
    as
    it
    was
    entered
    into
    without
    public
    notice
    and
    opportunity
    for
    comment.
    Second,
    while
    it
    states
    on
    its
    face
    the
    JEPA
    is
    to
    take
    certain
    actions,
    it
    is
    uncontroverted
    that
    JEPA never
    included
    any
    requirements
    in
    the
    Joliet
    land
    application
    permit
    that
    limited
    the
    quantity
    of
    radium
    applied
    to
    farm
    fields
    until
    October
    of
    2006 some
    twenty
    two
    years
    after
    it
    was
    signed.
    Joliet
    is
    not
    aware
    of
    any
    other
    permit
    with
    limits
    that
    predate
    its
    October
    2006
    pen-nit.
    Since
    Joliet
    was
    not
    a
    party
    to
    the
    inter-agency
    agreement,
    it
    was
    not
    possible
    to
    violate
    it
    directly.

    Joliet’s
    Subsequent
    Action
    On
    February
    28,
    2005,
    Joliet
    again
    submitted
    a
    new
    proposal
    for
    land
    application.
    This
    submittal
    is found in
    the
    Permit
    Record
    at
    R-
    104
    through
    R-29
    1.
    To prepare
    this
    submittal,
    Joliet
    had
    gathered
    a
    team
    of
    water
    supply
    engineers,
    wastewater
    treatment
    engineers,
    a
    consulting
    agronomist
    and
    a health
    physicist.
    The
    proposal
    is
    found
    in
    the
    Permit
    Record
    at
    R104
    through
    R-291.
    Although
    the
    proposal
    addressed
    the
    increase
    in
    radium
    concentration
    in
    the
    soil,
    the
    basis
    for
    the
    proposed
    1.0
    pico-curie
    per
    gram
    increase
    was
    the
    radiation
    dose
    received
    from
    this
    increase.
    The
    proposal
    was
    based
    on
    the
    Memorandum
    of
    Agreement,
    Paragraph
    7 which
    provides
    for
    alternative
    disposal
    methods
    when
    it
    is economically
    infeasible
    to comply
    with
    other
    paragraphs
    and
    the
    radon
    exhalation
    rate
    from
    the
    alternate
    disposal
    method
    is
    less
    than
    5.0
    pico-curies
    per
    square
    meter.
    Joliet
    employed
    RSSI,
    a
    consulting
    health
    physics
    firm
    to
    perform
    dose
    modeling
    of
    the
    application
    procedure
    to
    determine
    the
    dose
    to
    future
    residents
    of
    the
    currently
    agricultural
    land.
    RSSI
    used
    the
    RESRAD
    model
    to determine
    dose.
    The
    RESRAD
    computer
    code
    was
    developed
    in 1987
    by the
    Environmental
    Assessment
    Division
    at
    Argonne
    Laboratory and
    has
    undergone
    numerous
    revisions
    since.
    The
    code
    was
    used
    to
    predict
    the
    dose
    of
    radiation
    resulting
    from
    Joliet’s
    land
    application
    program.
    The
    inputs
    for
    radium
    concentration
    in
    sludge
    were
    the
    concentrations
    measured
    in
    the
    sludge
    from
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    and
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant.
    The
    models
    provided
    for
    8 applications
    of sludge
    over
    20
    years
    and
    9
    applications
    of sludge
    over
    22 years.
    RSSI
    used
    inputs
    provided
    by
    the
    City
    of Joliet
    to
    replace
    the
    default
    inputs.
    The
    input
    information
    was
    based
    on
    the
    number
    of
    homes
    per
    acre,
    size
    of
    home,
    type
    offoundation
    and
    the
    normal
    practice
    of
    removing
    expansive
    topsoil
    prior
    to construction.
    All
    models
    had
    results
    that
    residents
    would
    receive
    less
    than
    10
    milli-rems
    per
    year.
    Results
    are
    included
    in
    the
    record.
    The
    second
    part
    of the
    submittal
    included
    a report
    entitled
    “Evaluation
    of
    Radium
    Removal
    Impacts
    to
    Sludge
    Handling
    at
    the
    Eastside
    and
    Westside
    Wastewater
    Treatment
    Facilities”
    prepared
    by
    Clark
    Dietz,
    In.
    The
    report
    compared
    the
    costs
    of
    the
    current
    program
    of
    land
    application
    of
    liquid
    sludge
    to
    agricultural
    land
    with
    the
    costs
    of
    drying
    the
    sludge
    and
    landfill
    disposal.
    Page
    10
    (R288)
    provides
    Clark
    Dietz
    Inc.’s
    recommendation
    to
    continue
    with
    land
    application.
    This
    recommendation
    is
    supported
    by
    a
    comparison
    of
    life
    cycle
    costs
    for
    land
    application
    and
    landfill
    disposal.
    6

    The
    present
    value
    cost for
    the
    current
    land
    application
    program
    was
    $9,618,513
    based
    on
    2004
    dollars.
    For
    landfill
    disposal,
    the
    present
    value
    cost
    was
    $44,766,028.
    Landfill
    disposal
    increases
    the
    cost
    to
    Joliet
    by
    more
    than
    4
    times.
    Annual
    operating
    costs
    increase
    more
    than
    3.5
    times.
    This
    cost
    would
    directly
    impact
    the
    users
    of
    the
    system
    that
    would
    have
    to
    generate
    an
    additional
    $1,
    700,000
    per
    year.
    Part
    three
    of
    the
    submittal
    was
    a
    calculation
    of
    a cost
    to
    benefit
    ratio
    for
    the
    program.
    Since
    the
    savings
    to
    Joliet
    for
    a
    land application
    in
    lieu
    of
    landfill
    disposal
    was
    $36,147,515,
    this
    was
    treated
    as
    a
    benefit.
    It
    was
    adjusted
    for
    25
    years
    and
    increased
    to
    $40,140,326.
    The
    costs
    were
    developed
    using the
    Nuclear
    Regulatory
    Commission’s
    published
    costs
    for
    additional
    radiation
    exposure
    of
    $2,000
    per
    person-rem
    for
    1995.
    This
    cost
    was
    adjusted
    for
    inflation
    to
    $2,500 per
    person-rem
    in
    2004
    using
    the
    consumer
    price
    index.
    Based
    on
    the
    additional
    884.3
    person-rem
    of
    radiation
    exposure,
    a
    cost
    of
    $2,210.745
    was
    developed.
    A
    benefit
    to
    cost
    ratio
    using
    $40,140,326
    as
    the
    benefit
    and
    $2,210,745
    as
    the
    cost
    was
    developed.
    This
    ratio was
    18.16.
    This
    indicates
    to
    me
    that
    the
    benefits
    clearly
    outweigh
    the
    costs
    for
    Joliet.
    The
    fourth
    and
    final
    part
    of
    the
    submittal
    was
    the
    calculation
    of
    recommended
    increase
    in
    background
    radium
    concentration.
    Using
    10
    milli-rems
    per
    year
    as
    the
    limiting
    dose,
    and
    the
    dose
    from
    a
    single
    application
    of
    sludge
    from
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plan
    as
    1.48
    milli-rems
    per
    application,
    it
    was
    determined
    that
    6.76
    applications
    could
    be
    made
    to
    given
    field.
    6.76
    application
    of
    sludge
    with
    a 0.15
    pico
    curies
    per
    gram increase
    in
    background
    per
    application
    results
    in
    an
    increase
    in
    background
    of
    1.01
    pico-curies
    per
    gram.
    In
    real
    life,
    applications
    would
    have
    to
    be
    limited
    to
    6
    as
    it
    is
    not
    possible
    to
    make
    0.76
    of
    an
    application.
    This
    would
    result
    in
    an
    increase
    in
    background
    of
    0.90
    pido-curies
    per
    gram.
    IEMA-DNS
    Response
    (Record
    R-98
    through
    RiOl)
    Joliet
    did
    not
    receive
    a
    direct
    response
    from
    IEMA-DNS.
    Their
    response
    was
    directed
    to
    the
    Permit
    Section
    of
    the
    Division
    of
    Water
    Pollution
    Control.
    These
    comments
    were
    provided
    to
    Joliet
    in
    a
    May
    25,
    2005
    letter
    from
    Al
    Keller.
    It
    was
    requested
    that
    Joliet
    respond
    to
    the
    comments
    and
    provide
    copies
    of
    the
    response
    to
    both
    [EPA
    and
    JEMA
    DNS.
    Although
    the
    record
    does
    not
    include
    direct
    discussions
    with
    IEMA-DNS,
    Joliet
    met
    with
    IEMA-DNS
    to
    discuss
    the
    proper
    modeling
    approach
    to
    the
    issues
    raised.
    My
    calendar
    at
    Joliet
    has
    been
    eliminated,
    but
    I
    remember
    going
    to
    Springfield
    with
    Eli
    Port
    to
    meet
    with
    Rich
    Allen
    at
    his
    office
    in
    2005.
    Many
    of
    the
    issues
    raised
    by
    IEMA-DNS
    concerning
    permit
    limitations
    are
    normally
    handled
    by
    IEPA
    for
    other
    constituents
    in
    sludge.
    7

    Sludge Application
    Permit
    Renewal
    with
    Radium
    Limitation
    In
    October 2006, IEPA
    renewed
    Joliet’s
    permit
    for
    Land
    Application
    of
    Sewage
    Sludge,
    Permit Number
    2006-SC-4784.
    This
    permit
    contained
    Special
    Condition
    2;
    Sludge
    applied
    to
    land
    under
    this
    permit
    shall
    not
    cause
    the
    total
    accumulative
    increase
    of
    Radium
    226
    and
    Radium
    228
    in
    soil
    to
    exceed
    0.1
    pico-curies
    per
    gram.
    limiting
    radium
    concentration
    for
    the
    first
    time.
    Joliet determined
    that
    this
    condition
    would
    have
    the
    effect
    of
    limiting
    Joliet
    Westside
    Plant
    Sludge
    to
    one
    application
    per
    field.
    The single
    application
    of
    sludge
    to
    a
    field
    would
    disrupt
    the
    normal
    fertilizer
    program
    use
    by
    growers
    with
    very
    slight
    reduction
    in
    costs.
    This
    would
    result
    in
    the
    break
    down
    of
    Joliet’s sludge
    application
    program.
    Because
    Joliet
    thought
    this
    was
    an
    unworkable
    situation,
    Joliet
    contacted
    JEPA
    to
    begin to discuss
    a
    means
    of
    revising
    this
    condition.
    In
    response
    to
    a
    formal
    request
    seeking
    an
    extension
    of
    the
    permit
    appeal
    time
    deadline,
    IEPA submitted
    a
    Request
    for
    Ninety
    Day
    Extension
    of
    Appeal
    Period
    on
    behalf
    of JEPA
    and
    Joliet on
    November
    16,
    2006
    which
    was
    docketed
    by
    the
    Board
    as
    PCB
    07-38.
    A
    copy
    of
    this
    document
    is
    found
    as
    Exhibit
    ..
    As
    anticipated
    by
    this
    filing,
    Joliet
    continued
    to
    have
    discussions
    with
    1EPA
    as
    to
    how
    develop
    an
    agreeable
    means
    to
    allow
    Joliet
    to
    carry
    out
    its
    Sludge
    Disposal
    Program
    recognizing
    the
    IEPA’s
    need
    to
    regulate
    radium.
    Meeting
    about
    the
    0.1
    pico-curies
    per
    gram
    limitation
    On
    January
    24,
    2007
    Joliet
    met
    with
    JEPA
    and
    IEMA concerning
    this
    limitation
    of
    0.1
    pico-curies
    per
    gram. (Record
    at
    92-94)
    During
    the
    course
    of
    the
    meeting,
    Rich
    Allen
    of
    TEMA-DNS
    performed
    a “sum of
    the
    fractions”
    calculation
    and
    determined
    that
    0.4
    pico
    curies
    per
    gram
    could
    be
    supported.
    The
    sum
    of
    the
    fractions
    method
    is
    used
    for
    a
    mixture
    of
    radionuclides.
    The
    concentration
    of
    radium
    226
    is
    divided
    by
    the
    allowable
    concentration
    and
    the
    concentration
    of
    radium
    228
    is
    divided
    by
    the
    allowable
    concentration
    and
    the
    sum
    of
    those
    two
    fractions
    cannot
    exceed
    1.
    At
    the
    meeting,
    it was agreed
    that
    Joliet
    would
    receive
    0.4
    pico-curies
    per
    gram
    on
    a
    revised
    permit
    based
    on
    an
    anticipated
    revision
    to
    the
    Memorandum
    of
    Agreement
    by
    JEPA
    and
    IEMA-DNS.
    Other
    communities
    would
    also
    receive
    the
    0.4
    pico-curies
    per
    gram limitation
    on
    their permit
    renewals.
    IEPA
    list
    of
    communities
    (Record
    at
    R95-R96)
    The
    record
    includes
    a listing
    of
    the
    anticipated
    site
    life
    for
    radium
    applied
    to
    increase
    the
    background
    radium
    by
    0.4
    pico-curies
    per
    gram
    for
    various
    communities.
    It clearly
    demonstrates
    that
    Joliet
    is
    not
    the
    only
    community
    adversely
    impacted
    by
    this
    limitation.
    Channahon,
    Crystal
    Lake
    #3,
    Geneva,
    Huntley
    East,
    Huntley
    West,
    Kewanee,
    Lake
    in
    the
    Hills,
    Monmouth
    Main,
    and
    Yates
    City
    are
    other
    impacted
    communities.
    8

    January 24,
    2007 Meeting
    with
    IEPA,
    IEMA and
    Joliet
    (Record
    at
    R-92
    through
    R
    94)
    The
    January
    24,
    2007
    meeting
    was
    intended
    to
    determine
    the
    appropriate
    model
    for
    determining
    the
    allowable
    increase
    in
    radium
    above
    background.
    IEMA-DNS’s
    Rich
    Allen
    indicated
    that
    IEMA
    had
    two
    concerns,
    the
    allowable
    dose
    and
    correct field
    application.
    An
    allowable
    dose
    of
    10
    milli-rems
    per
    year
    was
    agreed
    upon
    by
    all
    present
    according
    to
    the
    meeting
    record
    prepared
    by
    Jeff
    Hutton.
    With
    this
    agreement
    in
    hand
    and
    based
    on
    previous
    work
    that
    had
    been
    performed
    by
    Joliet,
    I
    knew
    that
    a
    program
    limiting
    the
    dose
    to
    a
    future
    resident
    of
    land
    that
    had
    received
    sludge
    should not
    be
    a
    problem.
    Previous
    modeling
    had
    shown
    that
    10
    milli-rems
    per
    year
    was
    easily
    aéhieved
    with
    the
    assumption
    that
    no
    radium
    bearing
    soil
    remained
    directly
    under
    the
    house.
    At
    this
    meeting
    IEMA-DNS
    was
    concerned
    that
    an
    individual
    that
    violated
    the
    building
    code
    would
    become
    a
    risk
    for
    additional
    radiation.
    Rogina
    and
    Associates,
    Ltd.
    had
    performed
    a telephone
    survey
    of
    communities
    in
    Will
    and
    Kendall
    County
    to
    confirm
    that
    all
    building
    codes
    in
    place
    required
    removal
    of
    topsoil
    prior
    to
    construction.
    Rich
    Allen
    of
    IEMA-DNS
    did
    not
    think
    that
    Joliet
    was
    spending
    enough
    to
    deal
    with
    its
    radium
    sludge.
    My
    recollection
    is
    that
    a discussion
    led
    to
    Joliet
    investigating
    the
    blending
    of
    Eastside
    and
    Westside
    Sludge
    at
    an
    additional
    cost
    to
    limit
    the
    increase
    in
    background.
    I
    clearly
    left
    the
    meeting
    with
    the
    understanding
    that
    Joliet
    would
    prepare
    a report
    that
    addressed
    the
    allowable
    dose,
    the
    dose
    resulting
    from
    various
    application
    scenarios
    and
    confirm
    that
    building
    codes
    require
    topsoil
    removal.
    As
    an
    interim
    step
    to
    allow
    Joliet
    to
    continue
    to
    be
    able
    to
    manage
    its
    Sludge
    Application
    Program,
    JEPA
    agreed
    to
    raise
    the
    limit
    in
    Special
    Condition
    2
    to
    0.4
    pico-curies
    per
    gram.
    Joliet
    would
    appeal
    this
    limit
    and
    move
    forward
    to
    develop
    the
    supporting
    information
    to allow
    the
    IEPA
    to
    consider
    a
    higher limit.
    Sludge Application
    Permit
    Modification
    As
    was
    agreed
    upon
    at
    the
    January
    24,
    2007
    meeting,
    Joliet
    allowed
    the
    place
    holder
    appeal
    in
    PCB
    07-38
    to
    expire
    which
    resulted
    in Board
    dismissal.
    On
    February
    16,
    2007
    the
    TEPA
    issued
    a modification
    to
    Joliet’s
    Land
    Application
    of
    Sewage
    Sludge,
    Permit
    Number
    2006-SC-4784
    which
    included
    a revised
    Special
    Condition
    2
    to
    read
    “Sludge
    applied
    to
    land
    under
    this
    permit
    shall
    not
    cause
    the
    total
    accumulative
    increase
    of
    Radium
    226
    and
    Radium
    228
    in
    soil
    to
    exceed
    0.4
    pCi/g.”
    Joliet
    filed
    an
    appeal
    of
    this
    permit
    on
    March
    21,
    2007
    which
    was
    docketed
    as
    PCB
    07-94
    by
    the
    Board.
    A
    copy
    of
    this
    appeal is
    found
    as
    Exhibit
    Following
    this
    appeal
    the
    parties
    continued
    to work
    as
    agreed
    to in
    the
    January 24,
    2007
    meeting
    and
    JEPA
    did
    not
    proceed
    to
    file
    the
    Record
    in
    that
    case.
    9

    Report
    “Land
    Application
    of
    Radium
    Bearing
    Biosolids”(Record
    at
    R-39 through
    R-91)
    At
    the
    direction
    of
    the
    City
    of
    Joliet,
    Rogina
    &
    Associates,
    Ltd.
    prepared
    a
    report
    entitled
    “Land
    Application
    of
    Radium
    Bearing
    Biosolids”.
    This
    report
    was
    intended
    to
    address
    the
    issues raised
    at
    the
    January
    24,
    2007
    meeting.
    What
    follows
    is
    a
    summary
    of
    the
    report
    which
    I
    believe
    may
    help
    the
    Board
    in
    its
    review.
    The
    objective
    of
    the
    study
    as
    stated
    in
    the
    report was
    to
    propose
    a
    basis
    for
    criteria
    to
    be
    included
    in
    a
    revised
    JEPA-JEMA
    DNS
    Memorandum
    of
    Agreement.
    The
    criteria
    must
    allow
    for
    the
    continuation
    of
    land
    application
    of
    radium
    bearing
    bio-solids
    to
    provide
    crop
    nutrients
    at
    a reasonable
    cost
    to
    the
    wastewater
    agency
    and
    protect
    the
    public
    health
    of
    future
    residents
    of
    the
    land.
    Current
    regulations
    for
    biosolids
    are
    intended
    to
    protect
    the
    public
    health.
    The
    regulations
    address
    vector
    and
    pathogen
    control
    and
    limit
    cumulative
    loadings
    of
    specific
    pollutants.
    The
    regulations
    are entitled
    “The
    Standards
    for
    the
    Use
    or
    Disposal
    of
    Sewage
    Sludge”
    (Title
    40
    of
    the
    Code
    of
    Federal
    Regulations
    Part
    503).
    Radium
    is
    not
    included
    the
    federal
    regulations,
    but
    is
    addressed
    by
    IEPA’s
    implementation
    of
    the memorandum
    of
    agreement
    with
    IEMA-DNS.
    The
    current
    agreement
    provides
    for
    0.1
    pico-curies
    per
    gram
    increase
    in
    radium.
    The
    anticipated
    impact
    of
    sludge
    application
    on
    agricultural
    land
    is
    the
    future
    conversion
    of
    the
    land
    to
    residential
    use. Public
    health
    protection
    would
    require
    that
    the
    dose
    of
    radiation
    from
    the
    application
    be
    limited
    to
    protect
    the
    public
    health
    of
    the
    future
    residents.
    •At
    the
    meeting
    of
    January
    24,
    2007,
    TEPA
    and
    IEMA-DNS
    had
    discussed
    allowable
    dose
    and agreed
    on
    10
    milli-rems
    per
    year.
    Modeling
    is
    used
    to
    estimate
    the
    radiation
    dose.
    The
    RESRAD
    computer
    code was
    used
    for
    this
    purpose.
    IEMA-DNS
    used
    RESRAD
    with
    the
    assumption
    that
    the
    home
    was
    built
    on
    radium
    bearing
    topsoil
    to
    detennine
    for
    radium
    226
    a
    soil
    guideline
    of
    0.23
    pico-curies
    per
    gram
    and
    for
    radium
    228
    a
    soil
    guideline
    of
    0.15
    pico-curies
    per
    gram.
    To
    account
    for
    both
    raionuclides
    being
    presenting
    sludge,
    IEMA-DNS
    used
    the
    sum
    of
    the
    fractions
    based
    on
    equal
    parts radium
    226
    and
    radium
    228
    to
    determine
    the
    combined
    soil
    guideline
    of
    0.4
    pico-curies
    per
    gram.
    10

    The
    City
    of
    Joliet
    compared
    their
    program
    to
    the
    IEMA-DNS
    modeling
    and
    determine
    that
    modeling
    specific
    to
    the
    Joliet
    program
    was
    necessary.
    Inputs
    to
    RESRAD
    were
    adjusted
    to
    account
    for the
    Joliet
    program.
    Key
    inputs
    adjusted
    were
    as
    follows:
    1.
    Removal
    of
    radium
    bearing
    soil
    The
    local
    regulation for
    the
    construction
    of
    homes
    is
    through
    the
    local
    building
    code. Building
    codes
    typically
    require
    removal
    of
    topsoil
    prior
    to
    construction.
    Joliet
    has
    historically
    applied
    bio-solids
    in
    four
    counties.Rogina
    & Associates,
    Ltd.
    surveyed
    communities
    to
    determine
    their
    code
    requirements
    and
    none
    allowed construction
    on
    topsoil.
    The
    summary
    of
    the
    survey
    is found
    at R-42
    2.
    Food
    Sources
    The
    inputs
    were
    based
    on
    purchased
    vegetables,
    dairy
    products
    and
    seafood.
    Appendix
    B includes
    a
    side
    by
    side
    comparison
    of
    inputs
    used
    by
    IEMA-DNS
    and
    Joliet.
    Calculation
    of
    the
    dose
    was
    performed
    by
    RSSI,
    a radiation
    safety
    and
    radiological
    health
    consulting
    firm.
    Eli
    Port,
    principal
    health
    physicist
    is
    provided
    separate
    testimony.
    The
    direction
    given
    to RSSI
    was
    to
    estimate
    the
    radiation
    dose,
    that
    would
    result
    to
    a
    future
    on-site
    resident
    from
    the
    current
    Joliet
    program
    and
    alternate
    methods
    proposed
    by
    Joliet.
    RESRAD
    was
    used
    to
    estimate
    the
    dose
    from
    each
    application
    alternative
    using
    an
    application
    rate
    of
    3.5
    dry
    tons
    per
    acre
    and
    the
    following
    concentrations
    in
    sludge:
    Eastside
    Wastewater
    Treatment
    Plant
    Westside
    Wastewater
    Treatment
    Plant
    Radium
    226
    7.9
    pico-curies
    per
    gram
    Radium
    226
    17.6
    pico-curies
    per
    gram
    Radium
    228
    9.0 pico-curies
    per
    gram
    Radium
    228
    26.2
    pico-curies
    per
    gram
    The
    RESRAD program
    was
    also
    to
    be
    run
    for
    an
    alternative
    using
    the
    IEMA-DNS
    inputs,
    and
    model
    a house
    being
    built
    on
    topsoil.
    This
    was
    to
    run
    only
    for
    the
    alternative
    that
    demonstrated
    the
    highest
    dose.
    Radon
    resulting
    from
    the
    decay
    of
    radium
    was
    to be
    included
    in the
    dose.
    The
    results
    will
    be
    discussed
    later
    in
    this
    testimony.
    The
    land
    application
    of
    biosolids
    provides
    nutrients
    for
    growing
    corn
    and
    soybeans.
    Biosolids are
    applied
    at rates
    that
    match
    the
    agronomic
    need
    of
    the
    crop.
    Corn
    requires
    nitrogen
    for
    development.
    Biosolids
    are
    a source
    of nitrogen.
    Nitrogen
    in
    biosolids
    is
    normally
    between
    1%
    and
    6%
    on
    a dry
    weight
    basis.
    Commercial
    fertilizers
    provide
    between
    11%
    and
    82%
    nitrogen.
    Biosolids
    from
    the
    Joliet
    Eastside Wastewater
    Treatment
    Plant
    have
    averaged
    2.07%
    nitrogen
    over
    the
    three
    year
    period
    ending
    in
    2006.
    11

    The
    biosolids
    from
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    have
    averaged
    3.5%
    over
    the
    same
    period.
    The low
    proportion
    of
    nitrogen
    in
    Joliet Eastside
    Wastewater
    Treatment
    Plant
    biosolids
    has
    caused
    the
    liquid
    biosolids
    to
    be
    unable
    to
    provide
    the
    required
    nitrogen
    application
    rate
    because
    the
    soil
    cannot
    absorb
    the
    large
    quantity
    of
    liquid.
    Phosphorus
    is
    another
    crop
    need.
    Biosolids
    generally
    contain
    between
    0.8
    and
    6.1%
    phosphorus
    compared
    to commercial
    fertilizer
    with
    8-24%
    phosphorus.
    Joliet’s
    land
    application
    program
    is
    operated
    using
    contract
    services
    under
    the
    direction
    of
    the
    Plant
    Operations
    Division.
    The
    contract
    agronomist
    is
    responsible
    for
    coordinating
    the
    availability
    of land
    with
    grower/land
    owners,
    providing
    Joliet
    with
    a
    list
    of
    available
    sites
    for
    inclusion
    in
    the
    documents
    for
    bidding
    the
    application
    contract,
    performing
    the
    necessary
    soil
    tests,
    performing
    the
    necessary
    biosolids
    analysis,
    determining
    the
    application
    rate
    acceptable
    to
    the
    landowner/grower,
    providing
    direction
    to
    the
    land
    application
    contractor
    concerning
    application
    rates
    and
    coordination
    with
    the
    grower/landowner.
    Land
    Treatment
    Alternatives
    provides
    these
    services
    under
    a
    professional
    services agreement
    with
    the
    City
    of
    Joliet
    that
    is renewed
    annually.
    Contract application
    services
    are
    awarded
    through
    a
    competitive
    bidding
    process
    on
    an
    annual
    basis.
    The
    contractor
    provides
    transportation
    and
    application
    a
    unit
    price
    per
    gallon.
    Land
    is
    currently made
    available
    to
    either
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    or
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant.
    The Aux
    Sable
    Creek
    Wastewater
    Treatment
    Plant
    had
    its
    first
    land
    application
    in
    2007.
    and
    was
    not
    included
    in
    the
    report.
    Sites
    used
    by
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    are
    sites
    with
    good
    access
    and
    within
    a
    reasonable
    distance
    of
    the
    plant.
    In
    2006
    these
    sites
    averaged
    4.3
    miles
    from
    the
    plant.
    The
    same criteria
    applies
    to
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    that
    had
    an
    average
    distance
    of 2.5
    miles
    in
    2006.
    Application
    rates
    vary
    from
    0.7
    dry
    tons
    per
    acre
    to
    5.8
    dry
    tons
    per
    acre.
    For
    the
    three
    year
    period
    ending
    2006,
    the
    normal
    application
    rate
    is
    35
    dry
    tons
    per
    acre.
    Radium
    concentrations
    in the
    biosolids
    were
    7.9
    picô-curies
    per
    gram
    radium
    226
    and
    9.0
    pico
    curies
    per
    gram
    radium
    228
    for
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    based
    on
    the
    average
    of
    four
    samples
    collected
    between
    October
    22,
    2003
    and
    February
    7,
    2007.
    Based
    on
    an
    application
    rate
    of
    3.5
    dry
    tons
    per
    acre,
    the
    increase
    in concentration
    in
    the
    soil
    is
    0.014
    pico-curies
    per
    gram
    radium 226
    and
    0.016
    pico-curies
    per
    gram
    radium
    228.
    12

    For
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant,
    the
    radium
    concentration
    in
    the
    biosolids is
    17.6
    pico-curies
    per
    gram
    for
    radium
    226
    and
    26.2
    pico-curies
    per
    gram
    for
    radium
    228.
    At
    the
    3.5
    dry
    ton
    per
    acre
    application
    rate,
    the
    increase
    in
    soil
    concentration
    is 0.03
    1
    pico-curies
    per gram
    radium
    226
    and
    0.047
    pico-curies
    per
    gram
    radium
    228.
    To
    address
    the
    issues
    raised
    by
    IEMA-DNS,
    alternative
    land
    application
    programs
    were
    investigated.
    The
    application
    of
    biosolids
    on
    a
    particular
    pattern
    was
    proposed
    as
    one
    alternative
    and
    the
    application
    of
    biosolids
    blended
    from
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    and
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    was
    proposed
    as
    the
    other
    alternative.
    Pattern
    application
    provided
    for
    a
    field
    to
    receive
    1
    application
    of
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    biosolids
    followed
    by
    two
    applications
    of
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    biosolids.
    Costs
    were
    developed
    for
    this
    alternative
    using
    he
    information
    in the
    “Evaluation
    of
    Radium
    Removal
    Impacts
    on
    Sludge
    Handling
    at
    the
    Eastside
    Wastewater
    Treatment
    Plant
    and
    the
    Westside
    Wastewater
    Treatment
    Plant.
    These
    costs
    were
    adjusted
    by
    the
    consumer
    price
    index
    to
    2006.
    The
    additional
    mileage
    necessary
    to
    transport
    the
    biosolids
    to
    fields
    was
    based
    on
    $4.69
    per
    loaded
    mile
    taken
    from
    the
    “United
    States
    Department
    of
    Agriculture
    4th
    Quarter
    2006
    Grain
    Truck
    Cost
    Report”.
    No
    adjustment
    was
    necessary
    as the
    report
    was
    based
    on 2006.
    Blended
    biosolids
    provided
    for
    the
    application
    of biosolids
    blended
    from
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    and
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    biosolids.
    This
    program
    would
    be operated
    as follows:
    A
    biosolids
    mixing!
    storage
    tank
    would
    be
    constructed
    at
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    Biosolids
    produced
    at
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    would
    be
    trucked
    to
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    and
    pumped
    into
    the
    tank
    Biosolids
    produced
    at
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    would
    be
    added
    to
    the
    tank
    at
    the
    ratio
    of
    two
    parts
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    biosolids
    to 1
    part
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    biosolids.
    The
    mixing
    equipment
    would
    be
    operated
    to
    create
    a
    well
    mixed
    blend
    of
    biosolids.
    Biosolids would
    be
    trucked
    to
    the regular
    disposal
    sites
    of
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant.
    The
    costs
    of
    transportation
    from
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    to
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    were
    based
    on
    the
    $4.69
    per
    loaded
    mile.
    13

    Landfill
    disposal
    was
    the
    final
    alternative.
    The
    previous
    study
    by
    Clark
    Dietz
    served
    as
    the
    basis
    for
    the
    study
    of
    the
    alternative.
    Costs
    were
    adjusted
    to
    2006 using
    the
    Engineering
    News
    Record
    construction
    cost
    index
    for
    new
    construction
    and
    the
    consumer
    price
    index
    for
    operating
    costs.
    The
    comparison
    of
    alternatives
    required
    development
    of
    the
    radium
    concentration
    in
    the
    blended
    biosolids. The
    radium
    226
    concentration
    was
    11.08
    pico-curies
    per
    gram
    and
    the
    radium
    228
    concentration
    was
    14.69 pico-curies
    per
    gram.
    The
    quantities
    of
    biosolids
    applied
    from
    each plant
    were
    determined
    from
    2004,
    2005
    and
    2006
    applications.
    Transportation
    costs
    for
    the
    current
    program,
    pattern
    application
    and
    blended
    alternatives
    were
    developed.
    Implementation
    issues
    were
    reviewed
    for
    each
    alternative.
    Pattern
    application
    could
    be
    implemented
    without
    additional
    capital
    expenses.
    Application
    rates
    would
    require
    adjustment,
    no
    other
    implementation
    issues
    were
    considered.
    Blended
    biosolids
    required
    the
    construction
    of
    a new
    mixing/storage
    tank
    at
    the
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant.
    The
    construction
    cost
    of
    the
    tank,
    associated
    piping,
    mixing
    pumps
    and
    nozzles
    was
    estimated
    to
    cost
    $2,000,000.
    The
    anticipated
    design
    and
    construction
    was
    anticipated
    to
    require
    two
    years.
    Landfill disposal
    capital
    requirements
    were
    included
    in
    the
    Clark
    Dietz,
    Inc.
    report.
    Design
    and
    construction
    also
    requires
    two
    years.
    Costs were
    compared
    with
    the
    resulting
    present
    values
    Current
    Program
    $10,264,662
    Pattern Application
    $11,310,437
    Blended
    Application
    $13,188,567
    Landfill
    Disposal
    $48,083,408
    Radiation
    doses with
    topsoil removed
    were
    also
    compared
    for
    all
    the
    alternatives
    except
    Landfill Disposal
    The
    results were
    as
    follows:
    Current Program
    Eastside
    10
    applications
    2.3
    milli-rems
    per
    year
    Current
    Program
    Westside
    10
    applications
    5.25
    milli-rems
    per
    year
    Pattern
    Application
    9
    applications
    3.03
    milli-rems
    per
    year
    Blended
    Biosolids
    10
    applications
    3.27
    milli-rems
    per
    year
    All
    of the
    programs
    provide
    less
    than
    the
    10
    .milli-rems
    per
    year
    agreed
    by
    IEPA
    and
    IEMA-DNS.
    All
    these
    alternatives
    provide
    the
    nutrients
    to
    the
    crops
    that
    are
    expected
    from
    land
    applications.
    Site
    life
    is long
    enough
    to
    allow
    grower/landowners
    to
    maintain
    the
    fertility of
    the
    soil.
    14

    One
    of
    the
    other
    tasks
    that
    was
    requested
    of RSSI
    was
    to
    determine
    the
    dose
    if
    the
    topsoil
    was left
    in
    place
    under
    the
    house.
    RSSI
    reported
    that
    the
    dose
    from
    10
    applications
    of
    biosolids
    from
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    is
    15.36
    milli-rems
    per
    year.
    This
    dose
    occurs
    the
    first
    year
    after
    the
    10
    application
    and
    declines
    over
    time.
    Dr.
    Port
    and
    Dr.
    Toohey will
    address
    the
    public
    health,
    issues
    related
    to
    15.36
    milli-rems
    per
    year
    dose.
    The
    issue
    of
    land
    application
    of
    biosolids
    with
    a
    radium
    concentration
    greater
    than
    50
    pico-curies
    per
    gram
    was
    also-addressed
    in
    the
    report.
    I recommend
    that
    any
    new
    inter
    agency
    Memorandum
    of
    Agreement
    provide
    a
    specific
    procedure
    for
    review
    and
    criteria
    for
    approval
    of
    land
    application
    of
    material
    with
    a concentration
    greater
    than
    50
    pico
    curies
    per
    gram.
    The
    dose
    to
    a
    future
    resident
    has
    been
    used
    to
    determine
    the
    criteria
    for
    land
    application
    for
    biosolids
    with
    a
    concentration
    less
    than
    50
    pico-curies
    per
    gram
    and
    dose
    would
    be
    appropriate
    criteria
    for
    biosolids
    with
    a
    concentration
    greater
    than
    50
    pico
    curies
    per
    gram.
    The
    number
    of
    applications
    would
    have
    to
    be
    reduced
    to
    control
    the
    dose
    to
    a
    future
    resident.
    The
    report
    conclusions
    are
    as follows:
    -
    10
    applications
    of
    biosolids
    form
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    does
    not
    result
    in
    exposure
    greater
    than
    10 milli-rems
    per
    year
    to future
    residents
    - For
    homes
    built
    that
    do
    not
    follow
    local
    building
    codes
    and
    have
    topsoil
    under
    the
    home,
    the
    anticipated
    dose
    for
    10
    applications
    of
    biosolids
    from
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    is
    15.35
    milli-rems
    per
    year.
    The
    cumulative
    radium
    concentration
    in soil
    can
    exceed
    the
    0.4
    pico-curies
    per
    gram
    limit
    proposed
    by
    IEMA-DNS
    The
    dose
    from
    a
    soil
    concentration
    increase
    of
    0.780
    pico-curies
    per
    gram
    is
    5.25
    milli-rems
    per
    year.
    An
    additional
    increase
    in
    soil
    concentration
    is possible
    and
    the
    dose
    to
    future
    resident
    would
    still
    be
    less
    than
    10
    milli-rems
    per
    year.
    Programs
    that
    do
    not
    require
    the
    removal
    of
    topsoil
    from
    beneath
    the
    housç
    should
    be
    limited
    to
    0.4
    pico-curies
    per
    gram
    increase
    in
    soil
    concentration.
    Bio-solids
    with
    a concentration
    less
    than
    100
    pico-curies
    per
    gram
    may
    be
    land
    applied without
    a
    special
    review.
    On
    June
    29,
    2007,
    I sent
    a copy
    of
    the
    Rogina
    &
    Associates,
    Ltd.
    Report
    entitled
    “Land
    Application
    of
    Radium
    Bearing
    Biosolids
    to
    Jeff
    Hutton
    and
    IEMA-DNS.
    (Record
    at
    R39).
    15

    Jeff
    Hutton Analysis
    (Record
    at
    R-35
    through
    R37)
    Jeff
    Hutton
    of
    IEPA
    wrote
    a
    memorandum
    summarizing
    his
    comments
    from
    Joliet’
    s June
    2007
    submittal.
    Mr.
    Hutton
    provided
    10
    specific
    comments
    and
    also
    made
    conclusions.
    1.
    Comment
    number
    1
    addressed
    the
    fact
    that
    Joliet
    approaches
    the
    radium
    issue
    on
    the
    number
    of
    applications
    allowed
    while
    the
    JEPA
    is only
    concerned
    with
    assuring
    that
    radium
    dose
    is
    kept
    below
    a
    safe
    limit.
    Joliet
    is
    concerned
    with
    the
    number
    of
    applications
    because
    grower/l4ndowners
    are
    concerned
    about
    the
    number
    and
    timing
    of
    applications
    to
    assure
    that
    Joliet’s
    program
    is
    compatible
    with
    the
    fertilizer
    program
    than
    is
    used
    by
    the
    grower.
    Too
    few
    applications
    just
    disrupt
    a
    grower’s
    fertilizer
    program
    with
    very
    limited
    reduction
    in
    cost.
    2.
    The significant
    differences
    in
    Joliet’s
    and
    IEMA-DNS’s
    allowable
    soil
    concentrations
    are
    the
    second
    comment.
    The
    0.4
    pico-curies
    per
    gram
    is
    not
    the
    result
    of
    RESRAD
    modeling,
    but
    of
    the
    “sum
    of
    the
    fractions’
    calculation
    performed
    by
    IEMA.
    3.
    Comment number
    3
    is
    concerned
    with
    building
    construction
    practice.
    The
    discussion
    concerns
    whether
    or
    not
    the
    topsoil
    is
    removed
    prior
    to
    construction
    of
    a
    home.
    Joliet’s
    survey
    of
    communities
    and
    counties,
    common
    practice
    and
    a
    telephone
    survey
    of
    builders
    performed
    by
    IEPA
    all
    indicate
    that
    topsoil
    is
    removed
    prior
    to
    construction.
    4.
    Mr.
    Hutton
    comments
    the
    IEMA-DNS’s
    inputs
    appear to
    be
    based
    on
    a
    resident
    farmer
    rather
    than
    suburban
    development.
    5.
    The
    food
    sources
    for
    Joliet
    and
    IEMA-DNS
    are
    different.
    IEMA-DNS
    appears
    to
    use
    a
    homeowner
    that
    drank
    milk
    produced
    on
    site,
    ate
    meat
    grown
    on
    sites
    and
    consumed
    vegetables
    grown
    on
    site.
    Suburbanites
    don’t
    normally
    have
    a milk
    cow
    and
    grow
    meat
    and
    poultry
    on
    site.
    6.
    Mr.
    Hutton
    commented
    that
    Joliet
    assumed
    that
    residents
    would
    drink
    water
    from
    the
    public
    water
    supply,
    while
    many
    well
    and
    septic
    subdivisions
    are
    developed
    in
    Northern
    Illinois.
    The
    well
    and
    septic
    subdivisions
    make
    IEMA-DNS’s
    approach
    valid.
    It
    should
    be
    noted
    that
    I
    am
    not
    aware
    of
    a
    single
    well
    and
    septic
    subdivision
    that
    has
    developed
    on
    land
    that
    has
    received
    Joliet
    biosolids.
    All
    the
    development
    that
    I
    recall
    has
    developed
    on
    the
    public
    water
    supply.
    7.
    There
    is a
    significant
    difference
    in
    the
    way
    that
    Joliet
    and
    IEMA-DNS
    handled
    background
    radium.
    Mr.
    Hutton’s
    comment
    is
    that
    the
    only
    concern
    about
    the
    land application
    program
    was
    the
    increase
    above
    background.
    16

    8.
    Mr.
    Hutton
    extrapolated
    the
    dose
    based
    on
    larger
    increases
    in
    sOil
    concentration.
    If
    Joliet
    applied
    biosolids
    up
    to
    the
    1.0
    pico-curies
    per
    gram
    proposed
    limit,
    the
    dose
    would be
    6.7
    milli-rems
    per
    year
    for
    homes
    where
    the
    topsoil was
    removed.
    If
    the
    topsoil
    was not
    removed,
    the
    dose
    would
    increase
    to
    19.7
    milli-rems
    per
    year
    at
    a
    sOil
    concentration
    ofi
    .0
    pico-curies
    per
    gram.
    It
    should
    be
    noted
    that
    Joliet’s
    proposal
    is
    that
    programs
    that
    do
    not
    remove
    topsoil
    should
    be
    limited
    to
    0.4
    pico-curies
    per
    gram.
    An
    individual
    that
    did
    not
    comply
    with
    the
    building
    code
    would risk
    higher
    exposure.
    9.
    The
    limitation
    on
    applying
    biosolids
    with
    a
    concentration
    of
    greater
    than
    50
    pico
    curies
    per
    gram
    drew
    Mr.
    Hutton’s next
    comment.
    Mr.
    Hutton
    does
    not
    see
    a
    problem
    with
    the
    sludge
    concentration
    as
    long
    as
    the
    increase
    in
    soil
    concentration
    is
    not
    exceeded.
    Mr.
    Hutton notes
    that
    only
    three
    communities
    have
    reported
    concentrations
    approaching
    50
    pico-curies
    per
    gram.
    The
    communities
    are
    Joliet,
    Channahon,
    and
    Huntley.
    Other
    facilities
    that
    have
    not
    reported
    the
    radium
    concentration
    in their
    biosolids
    may
    also
    have
    high
    concentrations.
    10.
    Mr.
    Hutton
    notes that
    Mike
    Kiebe
    of
    IEMA-DNS
    was
    concerned
    that
    radium
    applications
    are
    not
    tracked
    by
    a
    central
    authority.
    If
    fields
    receive
    biosolids
    from
    multiple
    wastewater
    plants,
    no
    one
    may
    be
    monitoring
    the
    accumulated
    radium.
    Mr.
    Kiebe
    proposed
    a
    record
    keeping
    central
    authority
    and
    Mr.
    Hutton
    indicated
    that
    a
    tracking
    system
    may
    be
    necessary.
    Joliet
    will
    not
    apply
    biosolids
    to
    a
    field
    that
    has
    received
    biosolids
    from
    other facilities.
    This
    practice
    was
    not
    developed
    for
    radium,
    but
    for
    other chemical
    constituents
    to avoid
    a problem
    determining
    the
    source
    of
    a particular
    ëhemical.
    The,
    conclusion
    to
    Mr.
    Hutton’s
    memo indicates
    that
    1.0
    pico-curies
    per
    gram
    above
    background
    limitation
    and
    the
    removal
    of
    the
    topsoil
    under
    the
    structures
    would
    be
    protective
    of
    human
    health.
    He
    further
    states
    that
    this
    the
    limitation
    allowed
    by
    Wisconsin:
    A
    tracking
    data
    base
    is proposed
    by
    Mr.
    Hutton
    to avoid
    over—application.
    Mr.
    Hutton
    concludes
    that
    an
    allowable
    increase
    of
    1.0
    pico-curies
    per
    gram
    with
    topsoil
    removed
    should
    be
    proposed
    by
    JEPA.
    Apparently
    a
    presentation
    was
    made
    to
    IEMA-DNS.
    Mr.
    Kiebe
    of
    IEMA-DNS
    indicated
    to
    Mr.
    Hutton
    that
    IEMA-DNS
    has
    gone
    as
    far
    as
    they
    think
    they
    can
    by
    allow
    0.4
    pico
    curies
    per
    gram.
    Mr.
    Hutton’s
    observation
    is
    that
    the
    0.4
    pico-curies
    per
    gram is
    based
    on
    extremely
    conservations
    factors
    that
    do
    not
    appear
    to
    reflect
    the
    real
    world
    situation.
    Mr.
    Hutton
    identified
    inputs
    to
    the
    model
    that
    reflect
    the
    real
    situation.
    He
    also
    stated
    that JEPA
    should
    request
    that Joliet
    and
    TEMA-DNS
    should
    run
    the
    RESRAD
    model
    using the
    same
    inputs
    to
    determine
    the
    dose
    resulting
    from
    an
    increase
    of
    1.0
    pico-curies
    per
    gram..
    IEMA-DNS
    and
    IEPA
    should
    review
    Joliet’s
    proposal
    after
    the
    models
    are
    completed
    was
    the
    last
    recommendation
    of
    Mr.
    Hutton.
    17

    IEMA-DNS
    Response
    to
    Joliet’s
    Submittal
    (Record
    at
    R-33
    and
    R-34)
    and
    Joliet’s
    Response?
    IEMA-DNS
    responded
    on
    August
    13,
    2007
    in
    a
    letter
    to
    Mr.
    Toby
    Frevert.
    One
    of
    their
    comments
    was
    that
    Joliet
    misinterpreted
    the
    IEMA
    computer
    modeling.
    This
    may
    be
    correct.
    IEMA-DNS
    did
    obtain
    significantly
    different
    results
    than
    Joliet’s
    health
    physicist.
    IEMA-DNS
    is
    correct
    that
    Joliet
    took
    issue
    with
    1EMA-DNS’s
    failure
    to
    consider
    the
    removal
    of
    topsoil
    prior
    to
    construction.
    IEMA-DNS
    claims
    thatJoliet
    provided
    no
    documentation
    stating
    this
    requirement
    or
    documentation
    of
    procedures
    used
    by
    building
    inspectors
    to
    verify
    the
    topsoil
    removal.
    This
    demonstrates
    IEMA-DNS
    ‘s-
    separation
    from
    the
    real
    world.
    The
    International
    Building
    Code
    is
    a
    model
    building
    code
    that
    has
    been
    adopted
    throughout
    most
    of
    the
    United
    States.
    In
    the
    Midwest,
    it
    replaced
    the
    BOCA
    code
    that
    had
    been
    in
    use
    for
    many
    years.
    Both
    of
    these
    codes
    require
    the
    removal
    of
    topsoil.
    Building
    Inspectors
    require
    a
    visual
    inspection
    for
    a
    foundation.
    As
    a
    part
    of
    the
    foundation
    inspection,
    they
    visually
    observe
    that
    the
    topsoil
    has
    been
    removed.
    No
    particular
    note
    is
    made
    because
    the
    foundation
    would
    not
    be
    allowed
    to
    proceed
    if
    topsoil
    is
    still
    present.
    IEMA-DNS
    claims
    that
    Joliet
    did
    not
    provide
    input
    or
    output
    files
    so
    that
    IEMA-DNS
    could
    verify
    the
    results.
    Jiiputs
    are
    listed
    in
    the
    report.
    Output
    files
    were
    not
    provided
    because
    IEMA-DNS
    has
    the
    ability
    to
    independently
    verify
    the
    results
    using
    the
    same
    RESRAD
    program.
    IEMA-DNS
    takes
    the
    position
    thats
    a
    result
    of
    the
    increase
    to
    0.4
    pico-curies
    per
    gram,
    that
    Joliet
    would
    have
    to
    modify
    their
    program
    to
    meet
    this
    limit.
    JEMA-DNS
    apparently
    failed
    to
    consider
    that
    at
    the
    same
    meeting,
    it
    was
    agreed
    that
    10
    milli-rems
    per
    year
    was
    an
    acceptable
    dose.
    As
    a
    result,
    Joliet
    chose
    to
    continue
    to
    pursue
    a
    soil
    concentration
    that
    would
    match
    the
    10
    milli-rems
    per
    year
    dose.
    1EMA-DNS
    also
    misinterprets
    the
    blending
    and
    pattern
    application
    results.
    Both
    of
    these
    options
    had
    increases
    in
    cost
    from
    programs
    that
    were
    not
    good
    public
    policy.
    If
    10
    milli-rems
    is
    an
    acceptable
    dose,
    I
    don’t
    believe
    that
    additional
    expenses
    to
    achieve
    doses
    less
    than
    10
    milli-rems
    represent
    funds
    that
    are
    well
    spent.
    IEMA-DNS
    again
    raised
    the
    question
    of
    Joliet
    exceeding
    the
    01
    .pico-curies
    per
    gram
    limitation
    in
    the
    inter-agency
    memorandum
    of
    agreement.
    Joliet
    ‘s
    and
    other
    communities
    land
    application
    permits
    did
    not
    include
    a
    radium
    limitation
    for
    may
    ‘ears.
    Joliet’s
    first
    radium
    limitation
    was
    0.1
    pico-curies
    per
    gram
    in
    the
    fall
    of
    2006.
    In
    early
    2007,
    that
    was
    increased
    to
    0.4
    pico-curies
    per
    gram.
    One
    application
    of
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    biosolids
    does
    not
    exceed
    the
    0.1
    pico-curies
    per
    gram
    limit.
    The
    reason
    that
    Joliet
    only
    had
    four
    sample
    results
    was
    that
    no
    sampling
    requirement
    was
    implemented
    in
    the
    earlier
    permits.
    18

    August
    14,
    2007
    Meeting
    TEPA,
    IEMA-DNS
    and
    Joliet
    met
    again
    on
    August
    14,
    2007.
    The
    meeting
    was
    intended
    to
    resolve
    open issues
    and
    receive
    a
    review
    of
    Joliet’
    s
    report.
    When
    IEMA-DNS
    arrived,
    they
    provided
    the
    August
    13,
    2007
    response
    to
    Joliet’s
    report
    which
    either
    IEPA
    or
    Joliet
    had
    seen.
    This
    was
    the
    first
    meeting
    that
    IEMA-DNS
    was
    not
    represented
    by
    Rich
    Allen
    as
    he
    was
    no
    longer working
    at
    IEMA-DNS.
    The
    meeting
    did
    not
    go
    well.
    IEMA-DNS
    felt
    that
    the
    Joliet
    report
    did
    not
    look
    at
    alternatives
    to
    the
    land
    application
    program.
    Joliet
    did
    not
    see
    IEMA-DNS
    giving
    good
    onsi4eration to
    the
    current
    program
    that
    met
    the
    agreed
    10
    milli-rems
    per
    year
    dose.
    IEMA-DNS
    seemed
    to
    take
    the
    approach
    that
    0.4
    pico-curies
    per
    gram
    had
    been
    approved
    at
    the
    previous
    meeting
    and
    that
    no
    further
    increase
    was
    possible.
    Joliet
    left
    the
    meeting
    with
    the
    idea
    that
    IEMA-DNS
    had
    reached
    their limit
    for
    adjustment
    to
    the
    soil
    concentration.
    It was
    agreed
    that
    RSSI
    and
    IEMA-DNS
    would
    meet
    and
    compare
    inputs
    to
    the
    RESRAD
    program.
    IEPA Requested
    Information
    from
    IEMA-DNS
    to
    clarify
    points
    from
    the
    Augustl4,2007
    meeting.
    Jeff
    Hutton sent
    a
    Memo
    to
    Mike
    Kiebe
    dated
    December
    3,
    2007
    in
    which
    he
    asks
    questions
    concerning
    the
    modeling
    of
    dose
    response(Record
    at
    R
    32):
    1.
    What
    soil
    concentration
    was
    used
    in
    the
    IEMA-DNS
    model,
    7.1,
    1.0
    or
    0;
    4
    pico
    curies
    per
    gram
    2.
    Were
    food
    inputs
    part
    of the
    IEMA-DNS
    model?
    3.
    What
    is the
    dose
    of
    an
    individual
    for
    an
    increase
    in
    the
    background
    of
    1.0
    pico
    curies
    per
    gram
    with
    topsoil
    removed
    and
    no
    food
    inputs.?
    4.
    What is the
    dose
    of
    an
    individual
    for
    an
    increase
    in
    background
    of
    1.0
    pico-curies
    per
    gram
    without
    the
    topsoil being
    removed
    and
    no
    food
    inputs?
    IEMA-DNS/RSSI
    Coordination
    Following the
    August
    2007
    meeting,
    IEMA-DNS
    and
    RSSI
    met
    and
    compared
    inputs
    to
    the
    RESRAD program.
    They
    obtained
    similar
    results
    for
    similar
    inputs.
    19

    James
    E
    Eggen
    Letter
    of
    December
    22,
    2007
    (Record
    R-26-R28)
    Mr.
    Eggen
    wrote
    a
    letter
    that
    summarized
    Joliet’s
    approach
    to
    resolving
    the
    issues.
    He
    identified
    IEMA-DNS’s
    refusal
    to
    accept
    that
    topsoil
    is removed
    prior
    to
    building
    construction
    as
    a
    major
    issue.
    He
    also
    indicated
    that
    IEMA-DNS
    and
    RSSI
    had
    met
    and
    IEMA-DNS
    agreed
    with
    the
    RESRAD
    results
    and
    said
    they
    would
    further
    review
    the
    data.
    After
    this
    discussion,
    IEMA-DNS
    drafted
    a
    revised
    memorandum
    of
    agreement
    based
    on
    0.4
    pico-curies
    per
    gram.
    Mr.
    Eggen’s
    conclusion
    was
    that
    IEMA-DNS
    and
    Joliet
    will
    not
    be
    able
    to
    come
    to
    a
    conclusion.
    Mr. Eggen
    encouraged
    JEPA
    to
    make
    an
    analytical
    interpretation
    of the
    City’s
    data
    and set
    a
    logical
    level
    of
    radium
    concentration.
    This
    appear&l
    to
    be
    Joliet’s
    only
    option,
    since
    IEMA-DNS
    was
    not
    demonstrating
    a
    willingness
    obtain
    a
    workable
    solution.
    Meeting
    between
    IEPA
    and
    IEMA-DNS
    (Record
    at
    R-23
    and
    R-24)
    In
    an
    effort
    to
    move
    the
    discussion,
    JEPA
    scheduled
    a
    meeting
    with
    JEMA
    on
    February
    26,
    2008.
    Marcia
    Wilhite,
    Manager,
    Bureau
    of
    Water,
    Sanjay
    Sofat,
    IEPA
    Attorney,
    Roger
    Selburg,
    Manager
    ,
    Division
    of
    Public
    Water
    Supplies,
    Alan
    Keller,
    Manager,
    Division
    of
    Water
    Pollution
    Control,
    Permit
    Section
    and
    Jeff
    Hutton,
    Permit
    Engineer
    went
    to
    the
    IEMA-DNS
    offices.
    IEMA-DNS
    was
    represented
    by
    Louise
    Michels
    and
    Michael
    Kiebe.
    The
    meeting
    notes
    indicate
    that
    the
    IEMA-DNS
    representatives
    would
    not
    be
    identified
    as
    “senior
    management”.
    Marcia
    Wilhite
    went
    over
    the
    major
    points
    on
    the
    agenda.
    1.
    the
    hearing
    process
    for
    a
    Joliet
    permit
    appeal,
    2.
    the
    status
    of
    the
    memorandum
    of
    agreement
    3. technical
    issues.
    Sanjay
    Sofat
    explained
    the
    Board’s
    permit
    appeal
    hearing
    process.
    The discussion
    of
    the
    technical
    issues
    and
    memorandum
    of
    agreement
    proceeded.
    Mr.
    Klebe
    indicated
    that
    slab
    on
    grade
    construction
    was
    a
    very
    conservative
    approach.
    Mr.
    Klebe
    stated
    that
    0.4
    pico-curies
    per
    gram
    is
    IEMA-DNS’s
    “comfort
    number”.
    Higher
    limits
    would
    require
    soil
    monitoring
    which
    is
    an item
    that
    IEMA-DNS
    does
    not
    want
    to
    do.
    20

    Mr.
    Kiebe
    also
    provided
    the
    information
    that
    if
    the
    topsoil
    is
    removed,
    IEMA-DNS’s
    model
    results
    in
    5.8
    milli-rems
    per
    year
    exposure.
    Mr.
    Klebe
    further
    indicated
    that
    Nuclear Safety
    does
    not
    want
    radium
    applied
    to
    land
    and
    0.4
    pico-curies
    per
    gram
    is
    what
    they
    would
    allow.
    The
    statement
    of
    Mr.
    Klebe
    don’t
    appear
    to
    represent
    a
    position
    of
    a state
    agency
    interested
    in
    providing
    safety
    and
    allowing
    the
    reuse
    of
    nutrients.
    IEMA-DNS
    was
    present
    at
    the
    meeting
    of
    January
    24,
    2007
    where
    it
    was
    agreed
    that
    10
    milli-rems
    per
    year
    was
    a
    safe
    dose.
    IEMA-DNS
    is
    ignoring
    the
    10
    milli-rems
    per
    year
    and
    arbitrarily
    deciding
    on
    a lesser
    dose.
    Request
    for
    Permit
    Modification
    Received
    July
    30,
    2008
    (Record
    at
    R-6
    through
    R
    8)
    As
    was
    discussed
    with
    IEPA,
    Joliet
    filed
    a
    Motion
    to
    Withdraw
    Permit
    Appeal
    in
    PCB
    2007-094
    which
    was
    granted
    by
    the
    Board.
    A
    Copy
    of
    this
    Motion
    is
    found
    as
    Exhibit
    There
    after
    Joliet requested
    on
    July
    29,
    2008
    a modification
    to
    permit
    No
    2006-4784-2
    concerning
    land
    application
    of
    biosolids.
    The
    reporting
    of
    radium
    results
    was
    requested
    to
    be
    extended
    to
    90
    days
    after
    sampling
    and
    the
    allowable
    increase
    of
    radium
    concentration
    over
    background
    was
    requested
    to
    be
    1.0
    pico-curies
    per
    gram
    in
    lieu
    of
    the
    limitation
    of
    0.4
    pico-curies
    per
    gram
    contained
    in
    Special
    Condition
    2.
    .The
    permit
    modification
    included
    the
    original
    Rogina
    &
    Associates,
    Ltd.
    Report
    entitled
    “Land
    Application
    of
    Radium
    Bearing
    Biosolids
    and
    Addendum
    1
    thereto.
    Addendum
    1
    Land
    Application
    of
    Radium
    Bearing
    Biosolids
    (Record
    at
    R-9
    through
    R-21)
    This addendum
    updated
    the
    quantities
    of
    biosolids
    applied,
    the
    radium
    concentration
    measured
    in
    the
    sludge
    and
    confirmed
    the
    amount
    of
    Joliet
    Eastside
    Wastewater
    Treatment
    Plant
    biosolids
    to
    the
    amount
    of
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    biosolids.
    The
    conclusions
    in
    the
    original
    report
    concerning
    allowable
    applications
    did
    not
    change.
    21

    IEPA
    Meeting
    and
    Permit
    Notes
    JEPA
    and
    the
    City
    of
    Joliet
    met
    on
    August
    28,
    2008
    to
    determine
    the
    best
    procedure
    for
    handling
    Joliet’s
    pending
    permit
    modification
    request.
    The
    agreed
    procedure
    included
    the
    following:
    1.
    IEPA
    would
    forward
    Joliet’s
    request
    to
    IEMA-DNS.
    2.
    The
    monitoring
    change
    would
    be
    acceptable,
    but
    the
    increase
    to
    1.0
    pico-curies
    per
    gram was
    unlikely
    to
    be
    approved.
    Joliet
    was
    concerned
    about
    the
    following:
    1.
    Did
    IEPA
    have
    anything
    in
    writing
    about
    10
    milli-rems
    per
    year
    being
    acceptable?
    2.
    Would
    IEMA-DNS
    be
    at
    the
    hearing?
    3.
    It
    was
    important
    for
    IEMA-DNS
    to
    be
    notified
    and
    provided
    with
    the
    documentation.
    Subsequent
    to
    the
    meeting,
    IEPA
    summarized
    their
    information
    for
    a permit
    decision.
    The
    discussion
    items
    are
    as
    follows:
    1.
    The
    request
    would
    allow the
    application
    of
    radium
    containing
    sludge
    that
    would
    raise
    the
    level
    to
    1.0
    pico-curies
    per
    gram
    above
    background.
    2.
    The
    sampling
    frequency
    would
    be
    changed
    to
    quarterly
    due
    to
    the
    time
    required
    for
    laboratory
    analysis.
    The
    notes indicate
    that
    the
    change
    is
    sampling
    frequency
    is
    acceptable.
    The
    notes
    also
    indicate
    that
    the
    increase
    to
    1.0
    pico-curies per
    gram
    would
    be
    in
    violation
    of
    the
    memorandum
    of
    agreement
    between
    IEPA
    and
    IEMA-DNS.
    The
    proposed
    actions
    were
    listed
    as
    follows:
    1.
    Deny the
    request
    for
    an
    increase
    above
    background
    2.
    Approve
    the
    request
    for
    monitoring
    change
    using
    a
    separate
    log
    number.
    22

    Denial
    Letter
    (Record
    at
    R-1)
    The
    final document
    is
    the
    denial
    letter
    that
    IEPA
    sent
    to
    Joliet.
    It
    lists
    the
    reason
    for
    denying
    the
    permit
    as
    the
    memorandum
    of
    agreement
    between
    the
    IEPA
    and
    IEMA-DNS
    which
    limits
    the
    increase
    in
    soil
    radium
    to
    0.1
    pico-curies
    per
    gram.
    Review
    and
    Summary
    Comments
    Without
    regard to
    the
    information
    presented
    by
    Joliet,
    IEPA
    believed
    it
    was
    required
    to
    deny
    Joliet’
    s
    request
    for
    an
    increase
    in
    the
    quantity
    of
    radium
    that
    could
    be
    applied
    with
    biosolids.
    The land
    application
    of
    biosolids
    has
    been
    a
    program
    that
    IEPA
    has
    encouraged
    as
    a
    disposal
    method.
    With
    this
    permit
    denial,
    it
    now
    appears
    that
    IEPA
    is no
    longer
    interested
    in
    land
    application.
    IEPA
    and
    IEMA-DNS
    prepared
    a
    memorandum
    of
    agreement
    in
    1981
    without
    giving
    the
    regulated
    community
    the
    right
    to
    review
    and
    comment
    upon
    it.
    The
    procedures
    for
    modeling
    radiation
    dose
    ‘have
    change
    tremendously
    since
    that
    time.
    The
    RESRAI
    computer
    model
    was
    not
    developed
    until
    1987
    and
    has
    been
    modified
    since
    1987.
    If
    10
    milli-rems
    per
    year
    is
    an
    acceptable
    dose,
    why
    is
    there
    such
    reluctance
    to
    allow
    programs
    that
    implement
    an
    acceptable
    dose.
    TEPA
    has
    been
    relying
    on
    IEMA-DNS
    to
    provide
    technical
    information.
    IEMA-DNS
    apparently
    has
    decided
    that
    no
    explanation
    of
    their
    decision
    to
    limit
    the
    increase
    to
    0.4
    pico-curies
    per
    gram
    is
    necessary
    as
    none
    has
    been
    provided
    to
    IEPA and
    none
    is
    set
    forth
    in
    the
    Permit
    Record.
    IEMA
    stated
    to
    TEPA
    that
    the
    removal
    of
    topsoil results
    in
    a
    dose
    of
    less
    than
    60%
    of
    the
    10
    milli-rems
    dose.
    It
    is
    common
    practice
    to
    rely
    on
    citizens
    to
    follow laws
    and
    regulations.
    IEPA
    accepts
    that local
    building
    codes
    and
    sound
    construction
    practice
    require
    removal
    of
    top
    soil
    before
    construction.
    IEMA-DNS
    seems
    convinced
    that
    buildings
    are
    routinely
    built
    without
    removing
    the
    topsoil as
    required
    by
    building
    codes.
    The
    modeling
    performed
    by
    RSSI and
    IEMA-DNS
    has
    shown
    that
    the
    dose
    from
    the
    failure
    to
    remove
    the
    topsoil
    is
    not
    extremely
    large.
    Ten
    applications
    of
    biosolids
    from
    the
    Joliet
    Westside
    Wastewater
    Treatment
    Plant
    would
    result
    in
    a dose
    of
    15.35
    milli-rems
    per
    year
    if
    the
    topsoil
    is left
    beneath
    the
    house.
    Most
    new
    construction
    in
    the
    Joliet
    area
    is a
    part
    of
    a
    40
    acre
    or
    larger
    subdivision.
    Common
    practice
    in
    developments
    of
    this
    size
    is
    to
    strip
    the
    topsoil
    from
    the
    site
    and
    place
    it
    in
    stockpiles
    during
    the
    grading
    and
    construction
    of
    the
    site.
    When
    the
    homes
    are
    ready
    for
    occupancy,
    the
    topsoil
    is
    spread
    on
    the
    lawn
    areas
    around
    the
    home.
    The City
    of
    Joliet
    Building
    Department
    reports
    that
    construction
    of
    home
    without
    obtaining
    permit
    is
    very
    rate.
    Dave
    Mackley,
    Director
    of
    the
    Department
    reports
    that
    in
    the
    23
    years
    that
    he
    has
    worked
    in
    Joliet
    that
    no
    one
    has
    attempted
    to
    build
    a home
    without
    a
    building
    permit.
    This
    has
    provided
    the
    opportunity
    for
    proper
    inspections
    including
    topsoil
    removal
    23

    The
    0.1
    pico-curies
    per gram
    limit
    will
    require
    Joliet
    to
    dispose
    of
    the
    biosolids
    in a
    landfill.
    The
    present
    value
    of
    a
    landfill
    disposal
    program
    is
    4.7
    times
    the
    cost
    of
    land
    application.
    This
    seems
    to
    me as
    waste
    of
    public
    funds.
    As
    Dan
    Fiedler
    indicated
    in
    his
    attachment
    to Harold
    Harty’s
    testimony,
    sampling
    of
    fields
    have
    indicated
    that
    variations
    in background
    radiation
    are
    greater
    than
    the
    1.0
    pico
    curies
    per
    gram
    that
    is
    of concern
    today.
    The
    Second
    Stated
    Basis
    for the
    Denial
    of
    the
    Modification
    Request
    JEPA
    cites
    a
    failure
    to
    comply
    with
    35
    Iii. Admin.
    Code
    Section
    309.241
    Standards
    for
    Issuance,
    as
    the
    other
    basis
    for
    its decision
    to
    deny
    Joliet’
    s
    permit
    modification
    request.
    This
    rule
    reads
    as follows:
    Section
    309.241
    Standards
    for Issuance
    a)
    The
    Agency
    shall
    not
    grant
    any
    permit
    required
    by
    this
    Subpart
    B,
    except
    an
    experimental
    permit
    under
    Section
    309.206,
    unless
    the
    applicant
    submits
    adequate
    proof
    that
    the
    treatment
    works,
    pretreatment
    works,
    sewer,
    or wastewater
    source
    will
    be constructed,
    modified,
    or
    operated
    so as
    not
    to
    cause
    a
    violation
    of
    the
    Act or
    of this
    Subtitle
    and
    b)
    If the
    Agency
    has promulgated,
    pursuant
    to
    Section
    309.262,
    criteria
    with
    regard
    to any
    part
    or condition
    of
    a permit,
    then
    for
    purposes
    of permit
    issuance
    proof
    of
    conformity
    with
    the
    criteria
    shall
    be
    prima
    facie
    evidence
    of no
    violation.
    However,
    non-conformity
    with
    the
    criteria
    shall
    not
    be grounds
    for permit
    denial
    if
    the
    condition
    of
    subsection
    (a)
    of
    this
    section
    is
    met.
    There
    is
    nothing
    in
    the
    Permit
    Record
    which
    supports
    this
    determination
    other
    that
    a
    reliance
    on
    the
    Memorandum
    of
    Agreement.
    The
    record
    is
    completely
    devoid
    of
    any
    concern
    or
    allegation
    of
    a violation
    of the
    Act
    or
    any
    applicable
    regulation.
    Joliet’s
    land
    application program
    follows
    the
    applicable
    environmental
    requirements
    concerning
    set
    backs
    from
    streams,
    roads
    and buildings
    to prevent
    any potential
    violation
    of
    the
    Act
    or
    the
    regulations.
    Joliet
    has
    completely
    and
    consistently
    complied
    with
    all
    applicable
    permitting
    requirements
    related
    to land
    application.
    Apart
    from
    the
    Memorandum
    of
    Agreement, IEPA
    has
    not cited
    any
    criteria
    related
    to radium
    in
    either
    the
    Act
    or
    the
    regulations
    adopted
    by
    the
    Board,
    or
    its
    own
    rules
    for
    that
    matter,
    because
    none
    have
    ever
    been
    enacted
    or adopted.
    24

    Conclusion
    This permit
    appeal
    represents
    an opportunity
    to
    support
    a
    continuing
    re-use
    program
    without
    adverse
    impacts
    on the
    general
    public.
    The alternative
    is
    to
    require
    the
    expenditure
    of
    public
    funds
    for
    very
    limited
    change
    in
    the environment.
    The
    requested
    change
    to Condition
    2 to
    allow
    an
    increase
    above
    background
    of
    1.0
    pico
    curies
    per gram
    results
    in a
    dose that
    the
    parties
    agree
    is protective
    of the
    public
    health
    and should
    be
    approved.
    There
    is
    nothing
    in
    the
    record
    to support
    the
    JEPA’s
    decision
    to
    deny
    the
    request
    based
    upon
    the Memorandum
    of
    Agreement
    or
    Section
    309.24
    1.
    CHO1/25277506.1
    25

    WRITTEN
    TESTIMONY
    OF
    ELI
    PORT
    IN
    THE
    MATTER
    OF
    City of
    Joliet
    v.
    Illinois
    EPA
    PCB
    09-25
    Before
    the
    Illinois
    Pollution
    Control
    Board
    Bolingbrook,
    Illinois
    January
    13,
    2009
    I
    am Eli
    A.
    Port.
    I
    hold
    a
    Master
    of
    Science
    degree
    in
    Health
    Physics
    from
    Northwestern
    University’s
    Environmental
    Health
    Engineering
    program.
    I
    am
    a
    Plenary
    Member
    of
    the
    Health
    Physics
    Society
    and
    I
    am
    certified
    by
    the
    American
    Board
    of
    Health
    Physics
    in
    comprehensive
    practice.
    Health
    Physics
    a
    scientific.
    and
    professional
    discipline
    which
    specializes
    in
    occupational
    and environmental
    radiation
    safety.
    Certification
    by
    the
    American
    Board
    of
    Health
    Physics
    indicates
    that
    a
    professional
    has
    met
    requirements
    for
    academic
    training
    and
    professional
    experience,
    and
    has
    passed
    an
    examination
    designed
    to
    test
    competence
    in
    this
    field
    of
    radiation
    protection.
    For
    the
    past
    33
    years,
    I
    have
    been employed
    by
    RSSI,
    6312
    West
    Oakton
    Street,
    Morton
    Grove,
    Illinois
    and
    I
    am RSSI’s
    president.
    Founded
    in 1976
    as
    Radiation
    Safety
    Services,
    mc,
    RSSI
    provides
    a
    wide
    range
    of
    occupational
    and environmental
    radiation
    protection
    services
    to
    clients
    in
    industry,
    business,
    government,
    medicine,
    education
    and
    law.
    RSSI provides
    program
    support
    to
    major
    corporations,
    not-for-profit
    research
    and
    academic
    institutions,
    and
    governmental
    agencies.
    In
    my
    work,
    I
    have provided
    radiation
    dose
    modeling
    for
    accident
    reconstruction,
    to
    demonstrate
    compliance
    with Federal
    and
    State occupational
    and
    environmental
    dose
    limits,
    and
    to
    determine
    pathways
    and
    public
    dose associated
    with spills
    and
    releases
    at
    nuclear
    power
    plants.
    I
    have
    developed
    United
    States
    Environmental
    Protection
    Agency
    (“U.S.
    EPA”)
    approved
    work
    plans and strategies
    to
    mitigate
    radium
    contamination
    in
    soil
    to
    U.S.
    EPA
    limits
    prior
    to
    development
    for
    residential
    use.
    I
    have
    been asked
    by
    the
    City of
    Joliet
    (“Joliet”)
    to
    study
    the
    potential
    health
    effects
    from
    naturally
    occurring
    radionuclides
    in
    waste
    water treatment
    sludge
    to
    support
    its
    efforts
    to
    continue
    its
    program
    to
    use
    this
    material
    on
    agricultural
    lands.
    The
    primary
    radionuclides
    of
    concern
    in
    sludge
    are
    the
    isotopes
    of
    radium
    (“Ra”)
    and their
    decay products.
    Radium
    is
    a
    naturally
    occurring
    radioactive
    element,
    present
    in
    rOck
    and
    soil
    and
    it
    may
    be
    found
    in
    groundwater.
    The
    more
    common
    isotopes
    of
    radium
    are
    Ra-226
    and
    Ra-228.
    Ra-226
    is
    the
    most
    important
    in
    terms
    of
    radiological
    health
    effects
    because
    of
    its
    decay
    kinetics
    and
    metabolism.
    Ra-226
    and
    Ra-228,
    collectively
    referred
    to
    as
    radium,
    both decay
    by
    emitting
    alpha
    particles
    to
    two
    series
    of
    naturally
    occurring
    radionuclides.
    Where
    radium
    is
    referred
    to
    in
    this
    testimony,
    it
    means
    the
    combined
    Ra-226
    and Ra-228.
    EBIJ

    Surface
    water
    usually
    has
    low
    radium
    concentrations,
    but groundwater
    concentrations
    can
    be
    significant.
    Water drawn
    from
    deep
    bedrock
    aquifers
    may contain
    concentrations
    of
    radium
    that
    exceed
    regulatory
    standards.
    In
    Joliet,
    and
    in
    most
    of
    Northern
    Illinois,
    high
    radium
    concentrations
    result
    from the
    presence
    of
    radium
    in
    the aquifers
    from which
    water
    supplies
    are
    withdrawn
    for
    public
    water
    supply.
    Radium
    iii
    drinking
    water
    may
    pose
    a
    radiological
    health
    hazard.
    About
    one-fifth
    of
    ingested
    radium
    is
    taken
    up
    by
    the
    body
    and the
    balance
    is
    excreted
    in
    feces.
    Some
    of
    the
    absorbed
    radium
    is
    subsequently
    excreted
    in
    urine.
    In
    the
    body,
    radium,
    a
    group
    hA
    alkali
    earth
    element,
    behaves
    like other elements
    in
    the
    group,
    such
    as
    calcium,
    and
    is
    deposited
    primarily
    in
    bone
    cortex.
    The
    internally
    deposited
    radium
    emits
    alpha
    particles
    that
    damage
    tissues
    adjacent
    to
    the
    decaying
    atoms.
    Radium
    is
    not
    known
    to
    cause
    adverse
    health
    effects
    at
    levels
    typically
    found
    in
    drinking
    water,
    diet,
    or
    the
    environment.
    The
    curie
    (“Ci”)
    is
    the
    unit
    used
    to
    quantify
    radioactive
    material.
    A
    subunit
    of
    the
    curie,
    the
    picocurie
    (“pCi”)
    is
    used
    in
    describing
    small
    quantities
    of
    radioactive
    material
    in
    environmental
    radiation
    protection.
    Studies
    of
    humans
    find
    that
    body
    burdens
    in
    excess
    of
    10
    .iCi
    result
    in
    an
    increased
    incidence
    of
    malignant
    disease.
    The
    U.S.
    EPA
    has
    established
    a
    maximum
    contaminant
    level
    (MCL)
    of 5 picocuries
    per
    liter
    (pCi/l)
    for
    radium
    in
    public
    water
    supplies.
    The
    MCL
    for
    radium
    has
    been
    set
    well
    below
    levels
    for
    which
    health
    effects have
    been
    observed
    and
    is
    assumed
    by
    the
    U.S.
    EPA
    to
    be
    protective
    of
    public
    health.
    Public
    water
    supply
    systems
    whose
    radium
    concentrations
    exceed
    5
    pCi/l
    are
    not
    known
    to
    be
    inherently
    unsafe,
    but
    are
    required
    to
    notify
    the
    public.
    These
    system&
    must
    also
    evaluate
    ways
    to
    reduce the
    radium
    concentrations
    in
    their water
    to
    comply
    with
    the
    MCL.
    The radium
    concentration
    in
    the
    Joliet
    water
    supply
    prior
    to
    treatment
    to
    remove
    radium
    is
    between
    6
    pCi/l
    and
    10
    pCi/I,
    exceeding
    the
    current
    MCL.
    Joliet
    now
    treats
    water
    to
    remove
    radium
    from
    drinking
    water
    in
    the
    supply
    system
    and
    transfers
    the
    radium
    to
    sewage
    treatment
    sludge.
    The radium
    bypasses
    human
    consumption
    and
    total
    amount
    of
    radium
    remains
    unchanged
    from historic
    values.
    Sludge
    is
    made
    available
    for agricultural
    application
    to
    exploit
    its nutrient
    content.
    The
    application
    of
    the
    sludge
    to
    land
    adds
    the
    radium
    in
    the
    sludge
    to
    the
    radium
    naturally
    in
    the
    soil
    or
    resulting
    from
    the
    prior
    applications
    of
    phosphate
    fertilizer.
    In
    2004,
    The
    City
    of
    Joliet
    has
    asked
    RSSI to
    model
    the
    increase
    in
    background
    dose
    to
    occupants
    of
    homes
    built
    on
    former
    agricultural
    land
    whose
    soils
    had
    been
    beneficially
    amended
    using
    sludge
    from
    waste
    water
    treatment
    plants.-
    RSSI
    selected
    the
    Argonne
    National
    Laboratory’s
    RESidual
    RADioactivity
    (RESRAD)
    Model,
    to
    assess the
    dose
    associated
    with
    residual
    radioactive
    material.
    RESRAD
    computes
    potential
    annual
    dose
    exposure
    to
    radioactive
    material
    in
    soil,
    and
    concentrations
    of
    radionuclides
    in
    air,
    surface
    water,
    and
    ground
    water
    resulting
    from
    the
    activity
    in
    soil.
    RESRAD
    RESRAD
    was developed
    to
    provide
    a
    scientifically
    based
    answer
    to
    the
    question
    “how
    clean
    is
    clean”
    and
    to
    provide
    useful
    tools
    for
    evaluating
    human
    health
    risk
    from
    residual
    contamination.
    RESRAD
    is
    used
    as
    a
    tool
    to
    evaluate
    radiologically
    contaminated
    sites
    and
    to
    support
    cost-
    benefit
    analyses
    that
    can
    help
    in
    decision-making.
    2

    RESRAD
    is
    widely
    used
    by
    government
    agencies
    in
    modeling
    dose
    from
    residual
    radioactive
    material
    in the
    environment
    and
    the
    Illinois
    Emergency
    Agency’s
    (“IEMA’s”)
    Division
    of
    Nuclear
    Safety
    used the
    RESRAD
    model
    in
    determining
    dose
    from
    radium
    on agricultural
    land
    converted
    to
    residential
    development.
    RESRAD
    allows
    for
    the
    setting
    of
    many parameters
    including
    radionuclide
    concentrations
    in
    soil,
    geologic
    characteristics,
    irrigation
    and
    run
    off, exposure
    and
    ingestion
    pathways,
    food
    production
    on
    the land,
    and
    building
    design,
    construction
    and
    use.
    The
    exposure
    pathways
    used
    by
    RSSI
    in
    the
    RESRAD
    modeling
    for
    land treated
    with
    sludge
    were
    direct
    external
    dose
    from
    the
    contaminated
    soil,
    and
    internal
    dose
    from
    inhalation
    of
    airborne
    radionuclides
    including
    radon
    progeny.
    The RESRAD
    model
    used
    by
    RSSI does
    not
    consider
    pathways
    that
    would
    not
    be
    likely
    in
    future
    urban
    or
    suburban
    residential
    use
    of
    land.
    The variables
    used
    as
    inputs
    were
    provided
    by
    the
    City
    of
    Joliet
    or,
    where
    data
    were
    not
    available,
    are
    RESRAD
    default
    values.
    Applications
    of
    sludge
    were
    at
    rates
    and
    using techniques
    specified
    by
    the City’s
    agronomist.
    Radium
    concentrations
    were
    typical
    of
    the
    sludge
    from
    the
    City’s
    plants.
    The
    City’s
    consultant
    and
    former
    Director
    of
    Public Works
    has
    conducted
    a
    survey
    of
    applicable
    municipal
    codes
    and
    county
    ordinances
    and
    reported
    that
    known
    codes
    and
    ordinances
    require
    the
    removal
    topsoil
    prior
    to
    construction.
    Accepted
    building
    techniques
    for
    houses
    to
    be
    constructed
    on
    land when converted
    to
    residential
    use
    also
    include
    removal
    of
    topsoil,
    whether
    the
    house
    is
    slab-on-grade
    or
    has
    a
    basement.
    In
    the
    model,
    the
    only
    interface
    with
    amended
    soil
    is
    the
    where
    topsoil
    is
    brought
    up
    against
    a
    basement
    wall or
    outside
    the
    home.
    RESRAD
    calculates
    that
    the maximum
    annual
    dose
    results
    from
    nine
    sludge
    applications
    of
    sludge
    adding
    0.058
    pCi/g
    Ra-226
    and
    0.091
    pCi/g
    Ra-228
    to
    the
    soil
    at
    each
    application.
    The
    nine
    applications
    increase
    the
    total
    radium
    concentration
    by
    1.34
    pCi/g
    and result
    in
    an
    annual
    dose
    less
    than
    9
    mrem
    per
    year.
    Nine
    mrem
    is
    less
    than
    one tenth
    the difference
    between
    the
    annual
    external
    natural
    background
    radiation
    in
    Joliet,
    125
    mrem!yr,
    and.
    Denver,
    250
    mrem.
    Nine mrem
    is
    one-quarter
    to
    one-third
    the
    annual
    dose
    from naturally
    occurring
    radionuclides
    in
    food,
    30
    mrem-35
    mrem,
    and
    less
    than one-twentieth
    the
    annual
    dose
    from
    radon
    in
    the
    average
    US
    home,
    200
    mrem.
    Tn
    2007,
    RSSI
    performed
    additional
    modeling
    using
    different
    application
    patterns
    and
    mixing
    depth.
    A
    resulting
    soil
    concentration
    of
    approximately
    half
    the
    2004
    values
    resulted
    in
    approximately
    half the
    dose,
    demonstration
    that
    the
    resulting
    dose
    is
    relatively
    insensitive
    to
    the
    depth
    radium
    is
    mixed
    in
    soil.
    JEMA
    performed
    RESRAD
    modeling
    using
    a
    higher
    concentration
    of
    radium
    in
    soil
    than
    could
    result
    from
    the
    Joliet
    program.
    IEMA
    very
    conservatively
    used
    parameters
    that
    included
    residents
    producing
    all
    of
    the
    fruit,
    vegetables,
    grain,
    meat,
    diary,
    poultry,
    fish
    and
    shellfish
    they
    consumed.
    The
    IEMA
    model
    was
    based
    living
    in
    a
    house
    built
    on
    agricultural
    topsoil,
    a
    practice
    the City’s
    consultant
    reported
    is
    inconsistent
    with
    modern
    building
    codes
    and
    practices.
    The
    very conservative
    JEMA
    model
    predicted
    a
    maximum
    175
    mrem.
    When
    the
    soil
    concentration
    used
    by TEMA
    is
    adjusted
    to
    the
    realistic
    concentration
    used
    by
    RSSI,
    the
    resulting
    maximum
    annual
    dose drops
    to
    25 mrem
    to
    residents
    who
    produce
    all
    of
    the
    fruit,
    vegetables,
    grain,
    meat,
    diary,
    poultry,
    fish
    and
    shellfish
    they consumed
    and
    live
    in
    a
    house
    built
    on
    agricultural
    topsoil.
    3

    IEMA
    requires
    that
    when
    land
    is
    released
    for
    unrestricted
    use,
    the
    residual
    radioactivity,
    excluding isotopes
    of
    radon,
    and
    their
    progeny,
    that
    is
    distinguishable
    from
    background
    radiation
    does
    not
    result
    in
    a
    dose
    to
    an
    average
    member
    of the
    critical
    group
    that
    exceeds
    25
    mrem
    per
    year,
    including
    that
    from
    groundwater
    sources
    of
    drinking
    water,
    and
    the
    residual
    radioactivity
    has
    been
    reduced
    to
    levels
    that
    are
    as
    low
    as
    reasonably
    achievable
    (ALARA).
    ALARA
    philosophical
    principal
    in
    radiation
    protection
    that
    means making
    every
    reasonable
    effort
    to
    maintain
    exposures
    to
    radiation
    as
    far
    below dose
    limits
    in
    as
    is practical
    consistent
    with
    the
    purpose
    for
    which
    an
    activity
    is
    undertaken,
    taking
    into
    account
    the
    state
    of
    technology,
    the
    economics
    of
    improvements
    in
    relation
    to
    the
    state
    of
    technology,
    the
    economics
    of
    improvements
    in
    relation
    to
    benefits
    to
    the
    public
    health
    and
    safety
    and
    other
    societal
    and
    socioeconomic
    considerations.
    Where doses
    are
    low,
    ALARA
    balances
    benefits
    and
    costs.
    ALARA
    does
    not
    mandate
    the
    lowest
    possible
    doses
    below
    the
    limits
    in standards
    and
    regulations.
    The
    U.S.
    EPA
    uses
    an
    Applicable
    or
    Relevant
    and
    Appropriate
    Requirement
    (ARAR)
    of
    5
    pCi/g
    combined
    radium
    is
    soil
    above
    the
    background
    concentration
    of
    radium
    in
    soil
    for
    unrestricted
    residential
    use.
    In
    its
    analyses,
    the
    U.S.
    EPA
    uses
    an
    average
    radium
    concentration
    of
    2.1
    pCi/g in
    soil.
    The
    Health
    Physics
    Society’s
    Position
    Statement
    “Radiation
    Risk
    in
    Perspective”,
    (attached
    as
    Exhibit
    X)
    states,
    “...for
    populations
    in
    which
    almost
    all
    individuals
    are
    estimated
    to
    receive
    a
    lifetime dose
    of
    less
    than
    10
    rem
    above
    background,
    collective
    dose
    is
    a
    highly
    speculative
    and
    uncertain
    measure
    of risk
    and
    should
    not
    be
    used
    for
    the
    purpose
    of
    estimating
    population
    health
    risks.” At
    9
    mrem
    per
    year,
    1,100
    years would
    be
    required
    to
    accumulate
    a
    10
    rem
    dose.
    The
    maximum
    annual
    dose
    of
    9
    mrem
    includes
    the
    dose
    from
    radon.
    The
    calculated
    dose
    resulting
    from the
    application
    of
    sludge
    is low
    when
    compared
    with
    the
    dose
    from
    other
    natural
    sources.
    As
    a
    professional,
    I find
    that
    this
    dose
    to
    be
    ALARA.
    When
    the
    benefits
    to
    municipalities
    and
    farmers
    are
    considered,
    attempting
    to
    reduce
    the
    dose
    by
    inhibiting
    the
    application
    of
    sludge
    is
    not
    consistent
    with
    the
    ALARA
    principal.
    To
    be
    conservative,
    I
    recommend
    that
    application
    programs
    be
    continued
    providing
    that
    no
    program
    be
    permitted
    to
    add
    more
    than
    1 pCi/g
    of
    combined
    radium
    to
    soil
    in
    a
    field
    during
    the
    life
    of
    the
    program.
    This
    ALARA
    limit
    is
    only
    20%
    of
    the
    U.S.
    EPA’s
    ARAR
    for
    any
    use,
    including
    residential.
    H
    \HOMF\400001
    Health
    Phvsicsjohct
    Fli
    Port
    Nariate
    ri
    doc
    CHOI!
    25278540.1
    4

    WRITTEN
    TESTIMONY
    OF
    RICHARD
    E.
    TOOHEY,
    PH.D.,
    CHP
    IN
    THE
    MATTER
    OF
    City
    of
    Joliet
    v.
    Illinois
    EPA
    PCB
    09-25
    Before
    the
    Illinois Pollution
    Control
    Board
    Bolingbrook,
    Illinois
    January
    13,
    2009
    My
    name
    is
    Richard
    B.
    Toohey.
    I
    hold
    a Ph.D.
    degree
    in
    nuclear
    physics
    from
    the
    University
    of
    Cincinnati
    (1973)
    and
    I am
    certified
    in
    comprehensive
    practice
    by
    the
    American
    Board
    of
    Health Physics (1992,
    recertified
    1996,
    2000,
    2004.)
    My
    current
    position
    is
    Director
    of
    Dose Reconstruction
    Programs
    for
    Oak
    Ridge
    Associated
    Universities
    in
    Oak
    Ridge,
    Tennessee.
    These
    programs
    are
    supported
    by
    the
    National
    Institute
    of
    Occupational
    Safety
    and
    Health
    (NIOSH)
    and
    by
    the
    Defense
    Threat
    Reduction
    Agency
    (DTRA)
    to gather
    exposure
    data
    and
    provide
    estimates
    of
    radiation
    doses
    received
    by
    workers
    in the
    nuclear
    weapons
    complex
    and
    military
    personnel
    present
    at atmospheric
    nuclear
    weapons
    tests.
    For
    the
    year
    August,
    2008
    through
    July,
    2009,
    I am
    the
    President
    of
    the
    Health
    Physics
    Society,
    the
    U.S.
    professional
    society
    for
    specialists
    in
    radiation
    protection,
    with
    almost
    6,000
    members.
    I am
    also
    a member
    of
    the
    National
    Council on
    Radiation
    Protection
    and
    Measurements
    (NCRP),
    a
    Congressionally
    chartered
    organization
    of
    100
    members
    that
    is
    charged
    with
    advising
    the
    federal
    government
    on
    radiation
    protection
    standards,
    measurement
    techniques,
    radiation
    exposures
    and
    health
    risks.
    From
    1973
    to
    1987,
    I
    was
    a
    staff
    scientist
    at
    the
    Center
    for
    Human
    Radiobiology
    at
    Argonne
    National
    Laboratory,
    participating
    in
    the
    study
    of
    the
    effects
    of
    radium
    on
    exposed
    humans,
    primarily women
    who
    worked
    as
    luminous
    dial
    painters
    in
    the
    1920’s.
    I have
    previously
    testified
    before the
    Illinois Pollution
    Control
    Board on
    the
    health
    effects
    and
    risks
    of
    radium
    in
    drinking
    water
    on
    many occasions,
    involving
    variance
    petitions
    from
    communities
    in
    Northern
    Illinois,
    including
    the
    City
    of
    Joliet.
    The
    current issue
    before
    the
    Board
    is
    a
    petition
    by
    the
    City
    of
    Joliet
    to
    permit
    disposal
    of
    radium-containing
    waste
    sludge
    from
    the
    treatment
    of drinking
    water
    by
    application
    to
    agricultural
    land,
    resulting
    in
    a
    total accumulative
    increase
    of radium
    not
    to
    exceed
    1.0
    picocuries
    per
    gram
    (pCi/g)
    of
    soil.
    This
    level
    exceeds
    that
    in a
    memorandum
    of
    understanding
    between
    the
    Illinois Environmental
    Protection
    Agency
    (Illinois
    EPA)
    and
    the
    Division
    of
    Nuclear
    Safety
    of
    the
    Illinois Emergency
    Management
    Agency
    (IEMA)
    that
    was
    originally
    set
    at
    0.1
    pCi/g,
    but
    as
    I
    understand,
    is
    now
    0.4
    pCi/g.
    1

    The
    federal standards
    for
    radiation
    exposure
    to
    members
    of
    the
    public
    from
    environmental
    levels
    of
    radioactive
    materials
    resulting
    from
    technological
    uses,
    such
    as
    waste
    disposal,
    include
    a
    dose
    limit
    of
    15
    mrem per
    year under
    United
    States
    Environmental
    Protection
    Agency
    (U.S.
    EPA)
    regulations,
    25
    mrem
    per
    year
    under
    United
    Stated
    Nuclear
    Regulatory
    Commission
    (U.S.
    NRC)
    regulations,
    and
    100
    mrem
    per
    year
    under
    United
    Stated
    Department
    of
    Energy
    (U.S.
    DOE) regulations.
    The
    dose
    parameter
    used
    in these
    regulations
    is the
    total
    effective
    dose equivalent
    (TEDE),
    more
    recently
    referred
    to
    as
    effective
    dose,
    which
    includes
    external
    exposure
    to
    penetrating
    radiation
    (gamma
    rays)
    plus any
    internal
    exposure
    resulting
    from
    the
    inhalation
    or
    ingestion
    of
    radioactive
    materials.
    In
    addition,
    the
    internal
    component
    of
    the
    dose
    is
    integrated
    for
    a
    period
    of
    50
    years
    post intake,
    but
    assigned
    to
    the
    year
    of
    intake.
    The
    important
    thing
    to
    note
    is
    that
    the
    limits
    are
    for
    dose,
    because
    potential
    risks
    to human
    health
    from
    radiation
    exposure
    are
    assumed
    to
    be
    directly
    proportional
    to
    the
    radiation
    dose
    received.
    The
    secondary
    or
    derived limits
    for
    such
    quantities
    as
    the
    concentration
    of
    a
    radioactive
    isotope
    in
    drinking
    water,
    in
    air,
    or
    in
    soil
    are
    calculated
    by
    means
    of
    a
    pathway
    analysis,
    which
    determines
    the
    dose
    coefficient,
    i.e.,
    the
    dose
    per
    unit
    concentration
    of
    a
    given
    isotope
    in
    a
    given
    environmental
    medium.
    The
    concentration
    limit
    is then
    that
    concentration
    which
    results
    in
    the
    dose
    limit,
    when
    all
    pathways
    are
    included;
    this
    is
    equal
    to
    the
    dose
    limit
    divided
    by
    the
    dose
    coefficient
    for
    all
    pathways.
    In
    the
    case
    of
    disposal
    of
    radium-containing
    sludge
    on
    agricultural
    land,
    the
    pathways
    to
    be
    considered
    include
    direct
    gamma-ray
    exposure,
    inhalation
    of
    the
    radioactive
    material
    or
    its
    radioactive
    decay
    products,
    and
    ingestion
    of
    the
    radioactive
    material
    by
    direct
    ingestion
    of
    soil,
    or
    ingestion
    of
    foodstuffs
    or
    water
    which
    have
    absorbed
    the
    radioactive
    material
    from
    the
    soil.
    The
    radioactive
    isotopes
    to
    be
    considered
    in
    this
    case
    are
    Ra-226
    and
    Ra-228
    and
    their
    decay
    products,
    which
    includethe
    gamma-ray
    emitting
    isotopes
    Pb-214,
    Bi-214,
    and
    Pb-210
    from
    Ra
    226,
    and
    Ac-228, Pb-212,
    Bi-212,
    and
    Tl-208
    from
    Ra-228.
    Each
    radium
    isotope
    also
    produces
    a
    gaseous
    decay product:
    Rn-222
    from
    Ra-226,
    and
    Rn-220
    from
    Ra-228.
    The
    isotope
    Rn-220
    has
    a very
    short half-life,
    only
    55
    seconds,
    and
    so
    does
    not
    build
    up
    to
    appreciable
    levels.
    In
    contrast,
    the
    isotope
    Rn-222
    has
    a
    3.64-day
    half-life,
    and
    can
    move
    through
    soils
    into
    the
    living
    space
    of
    a
    house
    built
    on
    the
    soil;
    this
    isotope
    is
    in
    fact
    the
    contributor
    of
    most
    (about
    70%)
    of
    the
    effective
    dose
    from
    Ra-226
    in
    soil.
    However,
    if
    the
    topsoil
    containing
    the
    Ra-226
    is removed
    before
    house
    construction,
    then
    this
    pathway
    no
    longer
    exists.
    In
    addition,
    in
    a
    suburban
    environment,
    drinking
    water
    and
    the
    majority
    of
    foodstuffs
    typically
    do
    not
    comç
    from
    the
    homeowner’s
    property,
    and
    so
    the
    ingestion
    pathways
    for
    food
    and
    water
    are
    also
    not
    applicable.
    Based
    on
    the
    pathway analyses
    previously
    submitted
    by
    the
    City
    of
    Joliet,
    I calculate
    a
    dose
    coefficient
    of
    25
    mrem per
    year
    per
    pCi!g
    of
    combined
    Ra-226
    and
    Ra-228
    in
    soil
    including
    all
    pathways,
    and
    a
    dose
    coefficient
    of
    7
    mrem
    per
    year
    per
    pCi/g
    combined
    radium
    if
    the
    Rn-222
    inhalation
    and
    the
    foodstuff
    and
    water
    ingestion
    pathways
    are
    excluded.
    Taking
    a conservative
    dose
    limit
    of
    10
    mrem
    per
    year,
    the
    all-pathway
    analysis
    would
    result
    in
    a
    concentration limit
    of
    0.4
    pCi/g,
    while
    the
    restricted
    pathway
    analysis
    would
    result
    in
    a concentration
    limit
    of
    1.4
    pCi/g.
    Under
    the
    restricted
    pathways,
    a
    concentration
    of
    1.0
    pCi/g
    would
    produce
    an
    annual
    dose
    of
    7
    mrem.
    To
    put
    this
    dose
    in
    perspective,
    the
    average
    U.S.
    resident
    receives
    an
    annual
    dose
    of about
    2

    300
    mrem
    per
    year
    from naturally
    occurring
    sources,
    of
    which
    200
    mrem
    result
    from
    the
    average
    indoor
    level of
    Rn-222,
    about
    1.0
    pCi/liter
    of
    air.
    In
    addition
    the
    average
    U.
    S.
    resident
    receives
    another
    240
    mrem
    from man-made
    sources,
    predominately
    medical
    uses. Twenty
    years
    ago,
    the
    average
    annual
    radiation
    dose
    from medical
    procedures
    was
    about
    60
    mrem,
    but
    it has
    since
    increased
    to
    about 240
    mrem,
    primarily
    from computed
    axial
    tomography
    (CAT)
    scanning
    and
    fluoroscopically
    guided
    interventions,
    such
    as
    coronary
    angioplasty;
    consequently,
    the
    annual
    average
    radiation
    dose
    in
    the
    U.S. is
    about
    540
    mrem,
    including
    both
    natural
    background
    radiation
    and
    man-made
    (medical)
    sources.
    The
    average
    background
    concentration
    of
    Ra-226
    in
    soil
    in
    the
    U.S. is
    about
    1
    pCi/g,
    but
    this
    can
    vary
    bya
    factor
    of
    10
    or
    more
    in
    either direction
    depending
    on
    the
    underlying
    geology
    of
    the soil;
    the
    average
    in
    Illinois
    soils
    is
    about
    equal
    to
    the
    U.S. average
    (1.0
    pCi/g.)
    In
    comparison,
    the
    concentration
    of
    Ra-226
    in
    granite
    countertops
    can
    be
    as
    high
    as
    100
    pCi/g
    or
    more.
    Interestingly
    enough,
    most
    phosphate
    fertilizer
    comes
    from
    phosphate
    rocks
    which
    contain
    from
    50
    to
    200
    pCi
    Ra-226
    per
    gram;
    although
    most of
    the
    radium
    is
    removed
    in
    the
    processing,
    a
    typical.
    radium
    concentration
    in
    fertilizer
    is
    27
    pCi
    per
    gram phosphate
    (P
    205
    ),
    so
    if
    a
    fertilizer
    is
    10% phosphate,
    the
    Ra-226
    concentration
    would
    be
    2.7
    pCi/g.
    Thus
    the
    normal
    agricultural
    application
    of
    fertilizer
    also
    increases
    the
    background
    concentration
    of
    Ra-226
    in
    soil.
    In
    setting
    standards
    for
    radiation
    exposure
    of
    the
    public,
    the
    effect
    of
    concern
    is
    cancer
    induction,
    and
    the
    U.S.
    EPA
    and
    other
    agencies
    apply
    what
    is
    called
    the
    linear
    no-threshold
    (LNT)
    model.
    Briefly,
    this
    model
    assumes
    that
    there
    is
    no
    threshold,
    that
    is,
    there
    is
    no
    level
    of
    exposure
    below
    which
    the
    effect
    can
    not
    occur;
    consequently,
    any
    exposure,
    no
    matter
    how
    small,
    is
    assumed
    to
    carry
    some
    risk
    of
    the
    effect.
    Secondly,
    the model
    assumes
    that
    the
    risk
    is
    linear,
    or
    directly
    proportional
    to
    the
    dose.
    As
    an
    example,
    consider
    a
    group
    of
    10,000
    people,
    each
    of
    whom
    receives
    a
    dose
    of
    1
    rem,
    or
    1,000
    mrem.
    Under
    thes.e
    circumstances,
    the
    cancer
    risk
    model
    used
    in
    radiation
    protection
    predicts
    that there
    would
    be
    5
    cases
    of
    radiation-induced
    cancer,
    in
    addition
    to
    a
    background
    incidence
    of
    4,000
    cancers
    without
    any
    radiation
    exposure.
    If
    the
    radiation
    dose
    were
    reduced
    to
    200
    mrem
    each,
    then
    there
    would
    be
    1 radiation-induced
    cancer.
    If
    the
    dose
    were
    reduced
    to
    the level
    proposed
    for
    radium-bearing
    sludge
    disposal,
    i.e.,
    7
    mrem
    per
    year,
    then
    we
    could
    expect
    1
    radiation-induced
    cancer
    to
    occur
    from
    about
    30
    years
    of
    exposure.
    Currently
    there
    is
    no
    way
    to
    predict
    which
    of
    the
    10,000
    exposed
    persons
    would
    be
    the
    one
    to
    incur the
    radiation-induced
    cancer,
    if
    indeed
    one were
    to
    occur.
    Regulators
    use
    this
    model
    to
    extrapolate
    from
    the
    observed
    risk
    at
    high
    levels
    of
    exposure,
    where
    we
    actually
    have
    human
    data,
    to
    a
    calculated
    risk
    at
    low
    levels
    of
    exposure,
    such
    as
    might
    occur
    from
    radium-containing
    sludge.
    According
    to
    the
    International
    Commission
    on
    Radiological
    Protection
    (ICRP),
    the
    risk
    coefficient
    used
    to
    estimate
    cancer
    risk
    is
    5%
    per 100
    rem,
    or
    0.0005
    per
    rem,
    or
    0.0000005
    per
    mrem,
    so
    the
    assumed
    risk
    from
    10
    mrem
    per
    year
    is
    0.000005,
    or
    5
    chances
    in
    1 million
    per
    year.
    This risk
    coefficient
    is
    based
    in
    large
    part
    on
    the
    follow-up
    of
    the
    Japanese
    atomic
    bomb
    survivors,
    with
    corrections
    made
    for
    differences
    in
    dose
    rate
    (instantaneous
    vs.
    prolonged),
    radiation
    types,.
    and
    background
    cancer
    rates
    in
    the
    Japanese
    and
    U.S.
    populations.
    Other
    studies
    of
    exposed
    human
    populations
    are
    also
    relevant
    to
    the
    radium-bearing
    sludge
    issue,
    especially
    the
    3

    follow-up
    studies
    of
    radium
    workers
    and,
    for
    Rn-222
    exposure,
    uranium
    miners.
    The
    data
    from
    the
    observed
    incidence
    of
    bone
    cancer
    in
    radium
    dial
    workers
    do
    not
    match
    the
    predictions
    of
    the
    LNT
    model.
    In
    my
    previous
    testimony,
    I
    showed
    that
    the
    radium
    dial
    painter
    data
    fit
    a
    different
    model,
    known
    as
    a
    quadratic
    model,
    and
    that
    the
    predictions
    of
    the
    LNT
    significantly
    over-estimate
    the
    risk
    of
    cancer
    induction
    at
    low
    levels
    of
    exposure.
    Later
    analyses
    of
    the
    data
    on
    the
    radium
    dial
    painters
    by
    Dr.
    RobertThomas
    showed
    that
    the
    data
    are
    in
    fact
    best
    fit
    by
    a
    cubic
    model,
    even
    farther
    away
    from
    theLNT
    model.
    One
    reason
    for
    this
    change
    is
    that
    the
    estimated
    intakes
    of
    radium
    by
    the
    dial
    painterswere
    previously
    underestimated.
    Thus,
    the
    same
    number
    of
    observed
    cancers
    was
    caused
    by
    higher
    radium
    intakes;
    consequently,
    regardless
    of
    which
    model
    is
    used,
    the
    risk
    per
    unit
    intake
    necessarily
    declines.
    Dr.
    Robert
    Rowland,
    formerly
    the
    director
    of
    the
    Center
    for
    Human
    Radiobiology,
    has
    summarized
    the
    Argonne
    radium
    studies
    in
    his
    book
    “Radium
    in
    Humans:
    A
    Review
    of
    U.S.
    Studies”
    (ANL/ER-3,
    1994.)
    The
    bottom
    line,
    however,
    is
    that
    the
    radium
    dial
    painter
    data
    show
    that
    the
    LNT
    model
    yields
    a
    gross
    over-estimate
    of
    the
    cancer
    risk
    from
    radium
    intakes.
    In
    addition,
    the
    dose
    and
    risk
    calculations
    in
    the
    RESRAD
    program
    include
    a
    high
    leukemia
    risk,
    based
    on
    the
    observed
    leukemia
    incidence
    in
    A-bomb
    survivors.
    However,
    there
    is
    no
    excess
    leukemia
    observed
    in
    the
    human
    radium
    workers,
    and
    so
    the
    RESRAD
    program
    over-estimates
    the
    true
    risk
    from
    Ra-226
    exposure.
    The
    risk
    of
    lung
    cancer
    from
    Rn-222
    exposure
    is
    based
    on
    long-term
    studies
    of
    uranium
    miners
    exposed
    to
    high
    concentrations
    of
    radon
    in
    the
    mines.
    Based
    on
    these
    data,
    the
    U.S.
    EPA
    considers
    radon
    exposure
    to
    be
    the
    second-leading
    cause
    of
    lung
    cancer,
    after
    tobacco
    smoking,
    responsible
    for
    some
    15,000
    cases
    of
    lungcancer
    per
    year.
    However,
    what
    EPA
    fails
    to
    emphasize
    is
    that
    90%
    of
    these
    cancers
    will
    occur
    in
    smokers.
    The
    uranium
    miner
    data
    clearly
    show
    that
    smoking
    and
    radon
    exposure
    act
    in
    a
    multiplicative
    fashion;
    the
    incidence
    of
    lung
    cancer
    in
    uranium
    miners
    who
    smoked
    was
    about
    ten
    times
    that
    in
    non-smoking
    miners.
    As
    smoking
    incidence
    continues
    to
    decrease
    in
    the
    U.S.
    population,
    the
    risk
    of
    cancer
    from
    radon
    exposure
    will
    also
    decrease.
    Of
    course,
    if
    radium-containing
    soil
    is
    removed
    from
    agricultural
    land
    prior
    to
    house
    construction,
    there
    is
    no
    risk
    from
    radon
    above
    background
    levels.
    There
    are
    three
    basic
    principles
    of
    radiation
    protection:
    justification,
    limitation
    and
    optimization.
    The
    principle
    of
    justification
    states
    that
    any
    radiation
    exposure
    must
    convey
    some
    benefit
    to
    an
    individual
    or
    to
    society
    as
    a
    whole
    in
    order
    to
    compensate
    for
    the
    assumed
    risk.
    The
    principle
    of
    limitation
    states
    that
    for
    a
    given
    type
    of
    exposure
    situation,
    there
    should
    be
    an
    upper
    limit
    that
    is
    not
    exceeded
    except
    in
    exceptional
    circumstances.
    The
    principle
    of
    optimization
    states
    that
    actual
    exposures
    should
    be
    held
    as
    far
    below
    the
    limit
    as
    reasonably
    achievable,
    taking
    into
    account
    economic
    and
    societal
    considerations.
    The
    benefit
    of
    medical
    radiation
    exposure
    is
    usually
    obvious
    in
    terms
    of
    diagnosis
    or
    treatment,
    but
    the
    benefits
    of
    other
    exposures
    may
    be
    more
    difficult
    to
    quantify.
    In
    the
    case
    of
    radium-bearing
    sludge
    disposal,
    the
    benefits
    could
    include
    lower
    cost
    of
    waste
    disposal
    for
    the
    municipality
    generating
    the
    sludge,
    and
    improvement
    of
    soil
    parameters
    for
    the
    farmer.
    The
    risk
    4

    however,
    may
    fall
    on
    a
    future
    occupant
    of
    the site,
    who
    was
    not a recipient
    of
    any
    benefit.
    Ironically,
    the
    risk
    to
    this
    individual
    arises
    from
    the
    risk
    reduction
    to
    the
    users of
    Joliet’s
    municipal
    water
    supply
    from
    removal
    of
    radium
    from their
    drinking
    water.
    If
    the
    occupant
    of
    the
    site
    were
    a
    drinking
    water
    consumer,
    the
    risk
    from the
    soil radium
    would
    be
    much
    less
    than
    the
    risk
    from consuming
    the
    drinking
    water
    containing
    the
    radium.
    The principle
    of
    limitation
    is
    reflected
    in
    the
    U.S.
    EPA
    standard
    of
    15
    mrem
    per
    year
    from environmental
    releases
    of
    radioactive
    materials,
    or
    in
    the
    limit
    of
    10
    mrem
    per
    year
    from
    radium-bearing
    sludge
    disposal
    proposed
    by
    the
    Illinois
    EPA.
    The principle
    of
    optimization
    comes
    in
    when
    considering
    the
    costs
    of
    sludge
    disposal
    by
    application
    to
    agricultural
    land
    vs.
    disposal
    in
    a landfill,
    if
    the radium
    concentrations
    are
    acceptable
    for
    landfill
    disposal,
    or
    in
    a
    radioactive
    waste
    repository,
    if
    the
    radium
    concentrations
    exceed
    the
    limits
    for
    a
    landfill.
    Optimization
    balances
    risk
    vs.
    the
    cost
    of
    avoiding
    the
    risk;
    in
    the
    case
    at
    hand,
    the
    risk
    from
    an
    additional
    dose
    of
    7
    mrem
    per
    year
    is
    minimal;
    this
    level
    of
    dose is
    well
    within
    the
    natural
    variation
    of
    background
    radiation
    doses
    across
    the
    U.S.
    and
    the
    world.
    It
    would
    also
    seem logical
    that
    because
    the
    risk
    from
    Rn-222
    can
    be
    eliminated
    by
    removal
    of
    top
    soil before
    housing
    construction,
    and
    that
    this
    practice
    is
    already
    required
    by
    municipal
    building
    codes,
    it
    would
    be
    within
    the
    purview
    of
    Illinois
    EPA
    to
    also
    require
    this
    practice
    in
    area
    where
    radium-bearing
    sludge
    has been
    deposited.
    It
    is a
    fact
    that
    it
    costs money
    to
    remove
    an
    environmental
    risk,
    and
    the total
    amount
    of
    money
    available
    to
    a
    municipality
    from
    tax revenues
    is
    limited.
    Buildings
    and
    roads
    must
    be
    maintained,
    schools
    and
    police
    and
    fire
    departments
    must
    be
    operated,
    and
    numerous
    other
    claims
    on
    the
    taxpayers’
    dollars
    exist.
    It
    is
    up
    to
    the
    taxpayers,
    through
    their
    elected
    representative.s,
    to
    determine
    the
    proper
    allocation
    of
    funds.
    We
    use
    risk
    analysis
    to
    estimate
    the
    risks
    of
    various
    environmental
    hazards,
    so
    that
    informed
    decisions
    can
    be
    made
    as
    to
    whether
    or
    not
    they
    are
    large enough
    to
    demand
    expenditure
    of
    public
    funds
    to
    correct.
    The
    Illinois
    EPA
    has
    the
    legal
    responsibility
    to
    make
    this
    determination
    and,
    like
    the
    U.S.
    EPA,
    uses
    the
    LNT
    model
    to
    estimate
    the
    magnitude
    of
    the
    risks.
    This
    approach
    has
    been
    endorsed
    and
    supported
    by
    both
    U.S. and international
    bodies
    concerned
    with
    setting
    standards
    for
    radiation
    exposure,
    including
    the
    NCRP
    and
    the
    ICRP.
    In
    1976,
    when
    the
    U.S. EPA
    issued
    its
    interim
    standards
    for
    radioactivity
    in
    drinking
    water,
    the
    maximum
    permissible
    concentration
    was
    set
    to
    be
    5
    pCi
    per
    liter
    for
    combined
    Ra-226
    and
    Ra-228;
    this
    level
    is
    still
    in
    effect.
    On
    July
    18,
    1991,
    U.S.
    EPA published
    in
    the
    Federal
    Register
    a
    notice
    of
    proposed
    rule-making
    for
    the
    final
    standards
    on
    radioactivity
    in
    drinking
    water
    that would
    increase
    the
    permissible
    levels
    for
    radium
    to
    20
    pCi
    per
    liter
    for
    Ra-226
    and
    Ra
    228
    separately.
    U.S.
    EPA
    made this
    recommendation
    because
    of
    better
    data available
    on
    risk
    modeling;
    previous
    U.S. EPA
    risk
    calculations
    had
    included
    a
    large
    risk
    àf
    leukemia
    induction,
    based
    on
    the
    experience
    of
    the
    atomic-bomb
    survivors,
    while
    the
    improved
    risk
    estimates
    lowered
    the
    leukemia
    risk
    to
    levels
    more
    consistent
    with
    the
    actual
    human
    data
    from
    radium
    workers.
    Unfortunately,
    Congress’
    renewal
    of
    the
    Safe
    Drinking
    Water
    Act
    prevented
    U.S.
    EPA
    from increasing
    the
    permissible
    levels
    of
    radium.
    Had
    U.S.
    EPA
    been
    able
    to
    do
    so,
    the
    problem
    of
    disposal
    of
    radium-bearing
    sludge
    would
    never
    have
    developed,
    because
    Joliet
    would
    not
    have
    been
    required
    to
    remove
    radium
    from its
    well
    water
    supply.
    In
    my
    testimony
    before
    the
    PCB
    5

    some
    15
    years
    ago,
    I
    advocated
    20
    pCi per
    liter
    of
    Ra-226
    as
    a
    reasonable
    level,
    even
    granting
    the
    LNT
    model
    used
    by
    U.S.
    EPA, and
    warned
    that
    setting
    the
    level
    at
    5
    pCi/L would
    result
    in
    unnecessary
    costs
    for
    treatment
    and
    waste
    disposal,
    which
    is
    the
    situation
    Joliet
    faces
    today.
    Nevertheless,
    the
    science
    has
    not
    changed;
    it
    is
    clear
    from
    the
    human
    data
    that
    the
    LNT
    model
    is
    conservative,
    that
    is,
    it
    overestimates
    the
    actual
    risk.
    Consequently,
    the
    calculated
    risk
    from
    disposal
    of
    radium-bearing
    sludge
    on
    agricultural
    land
    at
    a
    level
    that
    results
    in
    a
    radiation
    dose
    of
    10
    mrem
    per
    year
    or
    less
    is
    an
    extreme
    upper
    limit
    on
    the
    true risk,
    which
    may
    well
    be
    zero.
    The
    disposal
    of
    radium-bearing
    sludge
    on
    agricultural
    land
    with
    a
    total
    accumulative
    increase
    of
    radium
    not
    to
    exceed
    1.0 pCi/g
    of
    soil
    satisfies
    all
    three
    of
    the
    basic
    principles
    of
    radiation
    protection:
    justification,
    limitation,
    and
    optimization.
    Therefore,
    the
    petition
    of
    the
    City
    of
    Joliet should
    be
    granted.
    CHOI/
    25278334.2
    6

    RADIATION
    RISK
    IN
    PERSPECTIVE
    FOLJNDE
    15B
    SOC
    El
    1
    POSITION
    STATEMENT
    OF
    THE
    H
    EALTH
    HEALTH
    PHYSICS
    SOCIETY*
    PHYSICS
    SOCIETY
    Adopted:
    January1996
    Reaffirmed:
    March
    2001
    Revised:
    August
    2004
    Contact:
    Richard
    J.
    Burk,
    Jr.
    Executive
    Secretary
    Health
    Physics
    Society
    Telephone:
    703-790-1745
    Fax:
    703-790-2672
    Email:
    HPS@BurkInc.com
    http:!!www.hps,org
    In
    accordance
    with
    current
    knowledge
    of
    radiation
    health
    risks,
    the
    Health
    Physics
    Society
    recommends
    against
    quantitative
    estimation
    of
    health
    risks
    below
    an
    individual
    dose
    of
    5
    rem
    1
    in
    one
    year
    or
    a
    lifetime
    dose
    of
    10
    rem
    above
    that
    receivedfrom
    natural
    sources.
    Doses
    from
    natural
    background
    radiation
    in
    the
    United
    States
    average
    about
    0.3
    rem
    per
    year.
    A
    dose
    of
    5
    rem
    will
    be
    accumulated
    in
    the
    first
    17
    years
    of
    lfe
    and
    about
    25
    rem
    in
    a
    lifetime
    of
    80
    years.
    Estimation
    of
    health
    risk
    associated
    with
    radiation
    doses
    that
    are
    of
    similar
    magnitude
    as
    those
    received
    from
    natural
    sources
    should
    be
    strictly
    qualitative
    and
    encompass
    a
    range
    of
    hypothetical
    health
    outcomes,
    including
    the
    possibility
    ofno
    adverse
    health
    effects
    at
    such
    low
    levels.
    There
    is
    substantial
    and
    convincing
    scientific
    evidence
    for
    health
    risks
    following
    high-dose
    exposures.
    However,
    below
    5—10
    rem
    (which
    includes
    occupational
    and
    environmental
    exposures),
    risks
    of
    health
    effects
    are
    either
    too
    small
    to
    be
    observed
    or
    are
    nonexistent.
    In
    part
    because
    of
    the
    insurmountable
    intrinsic
    and
    methodological
    difficulties
    in
    determining
    if
    the
    health
    effects
    that
    are
    demonstrated
    at
    high
    radiation
    doses
    are
    also
    present
    atlow
    doses,
    current
    radiation
    protection
    standards
    and
    practices
    are
    based
    on
    the
    premise
    that
    any
    radiation
    dose,
    no
    matter
    how
    small,
    may
    result
    in
    detrimental
    health
    effects,
    such
    as
    cancer
    and
    hereditary
    genetic
    damage.
    Further,
    it
    is
    assumed
    that
    these
    effects
    are
    produced
    in
    direct
    proportion
    to
    the
    dose
    received,
    that
    is,
    doubling
    the
    radiation
    dose
    results
    in
    a
    doubling
    of
    the
    effect.
    These
    two
    assumptions
    lead
    to
    a
    dose-response
    relationship,
    often
    referred
    to
    as
    the
    linear,
    no-threshold
    model,
    for
    estimating
    health
    effects
    at
    radiation
    dose
    levels
    of
    interest.
    There
    is,
    however,
    substantial
    scientific
    evidence
    that
    this
    model
    is
    an
    oversimplification.
    It
    can
    be
    rejected
    for
    a
    number
    of
    specific
    cancers,
    such
    as
    bone
    cancer
    and
    chronic
    lymphocytic
    leukemia,
    and
    heritable
    genetic
    damage
    has
    not
    been
    observed
    in
    human
    studies.
    However,
    the
    effect
    of
    biological
    mechanisms
    such
    as
    DNA
    repair,
    bystander
    effect,
    and
    adaptive
    response
    on
    the
    induction
    of
    cancers
    and
    genetic
    mutations
    are
    not
    well
    understood
    and
    are
    not
    accounted
    for
    by
    the
    linear,
    no-threshold
    model.

    Radiogenic
    Health
    Effects
    Have
    Not
    Been
    Consistently
    Demonstrated
    Below
    10
    Rem
    Radiogenic
    health
    effects
    (primarily
    cancer)
    have
    been
    demonstrated
    in
    humans
    through
    epidemiological
    studies
    only
    at
    doses
    exceeding
    5—i
    0
    rem
    delivered
    at
    high
    dose
    rates.
    Below
    this
    dose,
    estimation
    of
    adverse
    health
    effect
    remains
    speculative.
    Risk
    estimates
    that
    are
    used
    to
    predict
    health
    effects
    in
    exposed
    individuals
    or
    populations
    are
    based
    on
    epidemiological
    studies
    -
    of
    well-defined
    populations
    (for
    example,
    the
    Japanese
    survivors
    of
    the
    atomic
    bombings
    in
    1945
    and
    medical
    patients)
    exposed
    to
    relatively
    high
    doses
    delivered
    at
    high
    dose
    rates.
    Epidemiological
    studies
    have
    not
    demonstrated
    adverse
    health
    effects
    in
    individuals
    exposed
    to
    small
    doses
    (less
    than
    10
    rem)
    delivered
    in
    a
    period
    of
    many
    years.
    Limit
    Quantitative
    Risk
    Assessment
    to
    Doses
    at
    or
    Above
    5
    Rem
    per
    Year
    or
    10
    Rem
    Lifetime
    In
    view
    of
    the
    above,
    the
    Society
    has
    concluded
    that
    estimates
    of
    risk
    should
    be
    limited
    to
    individuals
    receiving
    a
    dose
    of
    5
    rem
    in
    one
    year
    or
    a
    lifetime
    dose
    of
    10
    rem
    in
    addition
    to
    natural
    background.
    In
    making
    risk
    estimates,
    specific
    organ
    doses
    and
    age-adjusted
    and
    gender-
    adjusted
    organrisk
    factors
    should
    be
    used.
    Below
    these
    doses,
    risk
    estimates
    should
    not
    be
    used.
    Expressions
    of
    risk
    should
    only
    be
    qualitative,
    that
    is,
    a
    range
    based
    on
    the
    uncertainties
    in
    estimating
    risk
    (NCRP
    1997)
    emphasizing
    the
    inability
    to
    detect
    any
    increased
    health
    detriment
    (that
    is,
    zero
    health
    effects
    is
    a
    probable
    outcome).
    Imp
    act
    on
    Radiation
    Protection
    Limiting
    theuse
    of
    quantitative
    risk
    assessment,
    as
    described
    above,
    has
    the
    following
    implications
    for
    radiation
    protection:
    (a)
    The
    possibility
    that
    health
    effects
    might
    occur
    at
    small
    doses
    should
    not
    be
    entirely
    discounted.
    The
    Health
    Physics
    Society
    also
    recognizes
    the
    practical
    advantages
    of
    the
    linear,
    no-threshold
    hypothesis
    to
    the
    practice
    of
    radiation
    protection.
    Nonetheless,
    risk
    assessment
    at
    low
    doses
    shouldfocus
    on
    establishing
    arange
    of
    health
    outcomes
    in
    the
    dose
    range
    of
    interest
    and
    acknowledge
    the
    possibility
    of
    zero
    health
    effects.
    These
    assessments
    can
    be
    used
    to
    inform
    decision
    making
    with
    respect
    to
    cleanup
    of
    sites
    contaminated
    with
    radioactive
    material,
    disposition
    of
    slightly
    radioactive
    material,
    transport
    of
    radioactive
    material,
    etc.
    (b)
    Collective
    dose
    (the
    sum
    of
    individual
    doses
    in
    a
    defined
    exposed
    population
    expressed
    as
    person-rem)
    has
    been
    a
    useful
    index
    for
    quantifying
    dose
    in
    large
    populations
    and
    in
    comparing
    the
    magnitude
    of
    exposures
    from
    different
    radiation
    sources.
    However,
    collective
    dose
    may
    aggregate
    information
    excessively,
    for
    example,
    a
    large
    dose
    to
    a
    small
    number
    of
    people
    is
    not
    equivalent
    to
    a
    smalldose
    to
    manypeople,
    even
    if
    the
    collective
    doses
    are
    the
    same.
    Thus,
    for
    populations
    in
    which
    almost
    all
    individuals
    are
    estimated
    to
    receive
    a
    lifetime
    dose
    of
    less
    than
    10
    rem
    above
    background,
    collective
    dose
    is
    a
    highly
    speculative
    and
    uncertain
    measure
    of
    risk
    and
    should
    not
    be
    used
    for
    the
    purpose
    of
    estimating
    population
    health
    risks.
    2

    Footnotes
    ‘The
    rem
    is
    the
    unit
    of
    effective
    dose.
    In
    international
    units,
    1
    rem0.0
    1
    sievert
    (Sv)10
    mSv.
    References
    National
    Council
    on
    Radiation
    Protection
    and
    Measurements.
    Uncertainties
    in
    fatal
    cancer
    risk
    estimates
    used
    in
    radiation
    protection.
    Bethesda,
    MD:
    NCRP;
    NCRP
    Report
    No.
    126;
    1997.
    *
    The
    Health
    Physics
    Society
    is
    a
    nonprofit
    scientific
    professional.
    organization
    whose
    mission
    is
    excellence
    in
    the
    science
    and
    practice
    of
    radiation
    safety.
    Since
    its
    formation
    in
    1956,
    the
    Society
    has
    grown
    to
    approximately
    6,000
    scientists,
    physicians,
    engineers,
    lawyers,
    and
    other
    professionals
    representing
    academia,
    industry,
    government,
    national
    laboratories,
    the
    Department
    of
    Defense,
    and
    other
    organizations.
    Society
    activities
    include
    encouraging
    research
    in
    radiation
    science,
    developing
    standards,
    and
    disseminating
    radiation
    safety
    information.
    Society
    members
    are
    involved
    in
    understanding,
    evaluating,
    and
    controlling
    the
    potential
    risks
    from
    radiation
    relative
    to
    the
    benefits.Official
    position
    statements
    are
    prepared
    and
    adopted
    in
    accordance
    with
    standard
    policies
    and
    procedures
    of
    the
    Society.
    The
    Society
    may
    be
    contacted
    at
    1313
    Dolley
    Madison
    Blvd.,
    Suite
    402,
    McLean,
    VA
    22101;
    phone:
    703-790-1745;
    fax:
    703-790-2672;
    email:
    HPS@BurkInc.com.
    3

    Back to top