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PROPOSED PLAN Madison Metropolitan Sewerage District Superfund Site

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  • 8/11/2019 PROPOSED PLAN Madison Metropolitan Sewerage District Superfund Site

    1/8

    EPA

    United States

    Environmental Protection

    Agency

    Officeof

    Public Affairs

    Region5

    77 Wes t Jackson Blvd.

    Chicago, IL 60604

    Illinois

    Indiana

    Michigan

    Minnesota

    Ohio

    Wisconsin

    ;f 1

    3

    EPA

    Region5 Records Ctr.

    Public

    Comment Period

    235637

    U.S.

    EPA

    w i l l

    accept

    w r i tt e n

    comments

    on the

    Proposed

    Plan dur inga30-day p u b l i ccomment period from

    November

    18

    through

    December 18 ,

    1996.

    PublicMeeting

    U.S. EPAw i l l hold apub l ic meet ing toexpla in th e

    Proposed

    Plan and the other cleanup alternat ives

    consid-

    ered

    for the

    site. Oral

    and

    writ ten commentsw i l l

    b e

    acceptedat the mee t ing .

    e:

    Time:

    Place:

    Tuesday,

    No vember

    19 ,

    1996

    7

    p.m.

    Madiso n

    Mun i c i pa l

    B u i l d i n g

    R o o m L L l l O

    215

    Mart in Luther King,

    Jr .

    Boulevard

    Madison, Wisconsin

    PROPOSEDPLAN

    Madison

    Metropolitan

    Sewerage

    District

    Superfund Site

    BloomingGrove,

    Wisconsin

    November

    1996

    Introduction

    This Proposed Plan

    identifies

    the U.S.

    Environmental Protection Agen cy (U.S. EPA)

    cleanup recommendation

    for the

    Madison

    Metropolitan Sewerage District Superfund site

    (Madison M etro site)

    in

    Blooming Grove,

    Wisconsin(Figure 1). U.S.EPA isproposing

    Remedial Alternative 4(RA-4), w hich w ould

    includeconstru cting dikes, consolidating con-

    taminated

    sludge,

    an d

    covering

    the

    sludge

    wi th

    anapprov ed cap. Itw ould a lso include

    monitoring

    and

    m aintenance activit ies

    and

    future deed restrictions. U.S. EPA's recom-

    mendat ion

    is

    based

    on

    information collected

    dur ingthesite remedial investigation/feasibil-

    ity study(RI/FS)and a riskassessment,

    which evaluated potential

    health r isks

    posed

    by site contamination

    1

    .

    Public input on theal ternat ives and the infor-

    mat ion

    t h a t supportsthesealternativ es is an

    important

    contribut ion to the

    cleanupremedy

    select ion process. Based

    on new

    information

    or p u b l i c comment .U.S .EPA m ay modify

    the recommended

    al ternat ive orselect

    anoth-

    1

    Section 117 a)

    of theComprehensive Environmental

    Response.

    Compensation,a na

    Liao- i

    ty A ci

    iCERCLA) requires publication

    o f a

    nonce

    and a

    Proposed Plan for possible site remediation . Tne Propo sed Plan mustalso be made available to t^e public for com me nt Tnis Proposed Plan is a summary

    of in format ionincludedin the

    Feasibility

    Study Report Septem ber 1996) and other docum ents .n the

    Aa m m i s t r a t i ve

    Reco rd for the site Please consult the

    FeasibilityStudy Report a long

    w th the

    Admin is t r a t i ve Reco

    r

    ?

    for the

    si te,

    f or

    more deta i led rfo

    r

    rra:

    on

    - _ l

    /

    Treatment

    | | ^ s . Plant Facilities

  • 8/11/2019 PROPOSED PLAN Madison Metropolitan Sewerage District Superfund Site

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    eralternativepresentedin this

    planand/or

    the FSReport. The

    publicisencouraged toreview

    andcomment on all technolo-

    gies

    andalternatives considered

    for th e

    Madison Metro site.

    SiteBackground

    The

    Madison Metro site con-

    sistsof two lagoons that cover

    approximately 140acres. The

    lagoons were constructed in the

    1940sand

    1960s

    to

    provide

    storageforsew erage s ludge

    generated

    at the

    plan t . N ine

    Spr ings Creek f lows along th e

    south and east site borders.

    Several drainage ditches run

    along other site borders and

    empty in to

    the

    creek.

    T he

    sludge lagoon system

    at

    the s i te operated w ithou t prob-

    lems

    un t i l

    April 1970, when

    part of the Lagoon 2 dike col-

    lapsed, releas ing about

    85

    m i l -

    l ion gal lon s of the lagoon's

    conten ts to an adjacent d i tch .

    The Dis t r ic t subsequ ent ly

    repaired thed ike .

    N a t i o n w i d e concern arose

    abou t

    thepoten t i a l

    adverse

    env i ronmenta l and

    hea l th

    effects of po lych lor ina ted

    b i p hen y l s( PCBs) .

    w h i ch

    had

    been found in

    m u n i c i p a l s lu d g e

    in otherc o m m u n i t i e s . T h i s

    concern led theS e w e r ag e

    Dis t r i c t

    to beg in v o l u n t a r i l y

    a n a l v / i n i i i t s

    .sludge

    forP C B s .

    In late 1982, duringaroutine

    analysis

    of lagoon sludges, the

    District detected PC B concen-

    trations above

    50

    parts

    per

    mi l -

    l ion (ppm), th e legal l imit

    allowed by the federal Toxic

    Substances Control

    A ct

    (TSCA).

    Because th e District sold

    processed

    s ludgea s aferti l izer

    andsoilcondi tioner through

    its

    Metrogro program,sludges

    containing

    PCB

    concentrat ions

    above50 ppm were separated

    to prevent their use in the pro-

    gram. Farmers co nt in ue to use

    Metrogro sludge

    as a

    fer t i l izer ,

    butal l s ludge used is w ith in the

    regulatory

    l imit (below 50

    p p m )

    for PCB

    content .

    Hazard assessments conducted

    by

    U.S.

    EPA in

    1983

    an d

    1986

    determined lagoon s ludge s

    posed a potentia l threat to pu b-

    l ic heal th

    and the

    e n v i r o n m e n t .

    In 1990,

    th e

    site

    w as

    placed

    on

    U.S. EPA's Nat iona lPr ior i t ies

    List( N P L ) ,aroster ofhaz-

    ardous w as tes i tes e l ig ib l e for

    c l ean u p u n d e r the federal

    Super fund

    p r o g r a m .

    In

    J an u a r y

    1992, U.S . EPA and

    the Dis tr ic t s igned an

    agree-

    m e n t ,

    ca l led a Consen t Order ,

    r e q u i r i n g

    the

    Dis t r i c t

    toc o m -

    p le te

    a s t u d > d e f i n i n g the

    ex t en t o f con t amina t ion ( an RI )

    for the

    s i t e , f o l l owed

    bv a

    f e a -

    sibil i ty study (FS) to evaluate

    possible cleanup opt ions.

    After

    th e

    Distr ict comp leted

    the first

    round

    of RI

    sampling,

    U.S. EPArequested ad dit iona l

    sampl ing

    and

    monitor ing

    to

    more ful ly def ine s i te condi-

    tions.

    Thesetwo

    separate sam-

    pl ing

    eventsarereferred to as

    Phase

    I and

    Phase

    II of the RI.

    All U.S. EPA comments and

    data produced from Phase I and

    Phase

    II

    were incorporated into

    the final R I repor t , whichw as

    submit ted

    to

    U.S.

    EPA in

    September 1996.

    The RI

    indicated that PCBs

    were present in Lagoons 1 and

    2 at

    concentrat ions ran ging

    from

    1.1 to 17 0

    p p m .

    The

    h ighes t leve l s w ere de tec tedin

    the nor thw es t co rner of Lagoon

    2,

    w h e re

    the

    Dis t r ic t

    had

    at tempted tosegregate s ludge s

    w i t h the

    h i g hes t

    PCB

    co ncen -

    t ra t ions .

    L ow leve l sof vo la t i l e

    organicco m po unds ( VO Cs) ,

    one

    semiv o la t i l e o r gan ic co m-

    pound (SVOC) , pes t ic ides ,and

    severa l m e t a l s w e r e a l s o

    detected in s a m p l e sco l lec ted

    from

    L a g o o n s

    1 and 2.

    The RIalsoprov ided thef o l -

    l o w i n g in fo rma t io n :

    P C B s w e r ede tec ted i n t w o

    ot f ive pea t s am p lesfrom

    the

    bot tom of the lagoons ,

    b e n e a t h

    the

    s l u d g e .

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    Relatively low levels of

    VOCs,

    one

    SVOC, pesti-

    cides, and several metals

    were

    alsodetected in peat

    samples.

    PCBs,oneVOC,andsever-

    al metals w ere detected

    at

    low levels in all three

    lagoon sludge samples.

    Lowlevelsof one VOC and

    several metals were detected

    in

    ground-water

    samples.

    Low

    levels

    of

    PCBs

    were

    detected instream sedim ent

    samples.

    Following

    the RI, the

    District

    conducted

    a risk assessment.

    The risk

    assessment consisted

    of ahum an heal th evaluat ion

    and an

    ecological assessmen t,

    whichw ere used

    to

    assess re a-

    sonably anticipated

    future

    site

    w i t h regard

    to

    _ ian healthand ecological

    risks. The District submitted

    th e final risk assessment report

    to U.S.EPA inSeptember

    1996.

    The FS focused on the portions

    of the s i te conta in ing

    s ludge

    wi th PCB

    concen trations

    at or

    greater

    than 50 p p m . Dur ing

    the

    FS. 10cleanup a l ternat ives

    for th i s s ludge w eredeve loped

    and

    eva lua ted ,

    us ing the n in e

    e v a l u a t i on criteria l i s ted in

    Figure2.

    U.S.

    EPA has deter-

    mined that

    other

    sludges,w i th

    PCB

    concentrations below

    50

    ppm,can be safely managed

    throughaland application pro-

    gram.

    Summary

    of

    Site

    Rsks

    U.S. EPA is concerned abou t

    elevated

    concentrations of

    PCBs at the Madison Me tro

    site

    because long-term expo-

    suretoPCBs at

    those

    concen-

    trations

    could have adverse

    effects

    onhum an heal thand

    th eenvi ronment . D ur ingthe

    RI/FS,

    U.S.

    EPA determined

    that

    sludge

    hasbeen

    adequately

    containedin the lagoon system

    an d

    does

    notposerisks to

    humanhealth; how ever, con-

    servative assumptions indicate

    thatexposuretosludge con-

    ta in ing

    PCBconcen trations

    above 50 ppm could pose an

    ecological

    risk to

    area

    wi ld l i f e .

    PCBs canonl y have adverse

    effects

    through exposure,

    such

    astouchingcontaminated

    s ludgeor

    soi l , ing est ing con ta-

    minated

    part icles,

    or

    i n h a l i n g

    organic

    vapors . Al ternat ives

    developed

    for s i te c lean up

    inc ludem easures

    to

    reduce

    o r

    e l i m i n a t e the

    p o s s i b i l i t y

    of

    exposure

    to

    site

    con tam i n an t s .

    Summary of Alternatives

    As

    part

    of theRI/FS,U.S. EPA

    identif ied and

    evaluated alter-

    native s that could

    be

    used

    to

    address threats or potential

    threats posed by the site.

    U.S.

    EPAconsidered 10c l eanup

    action alternativesfor the site:

    N o Action (RA-1)

    RA- 1 involvesnoact ive

    cleanup

    or long-term manage-

    men t at the

    site.

    A

    No-Act ion

    alternative is

    required

    by law to

    give

    U.S.EPA abasisfo rcom-

    parison.

    Est imated

    Cost: 0

    Institutional

    Controls (RA-2)

    RA -2 involves dike construc-

    t ion to isolate andconsol idate

    s ludge containing PCB concen-

    t ra t ions

    at or

    above

    50

    p p m .

    This

    would facil i tate

    future

    remova l and land appl icat ion

    act iv i t ies

    fo r

    sludges contain-

    ing

    concentrat ions below

    50

    ppm. This alternative also

    i nvo lves the continuation of

    current

    rout inea ct iv i t i es,

    i n c l u d i n gs ludge managemen t ,

    main tenance

    of

    exis t ing ,natur-

    al vegetat ive

    cover ,

    d i ke

    mon i -

    tor ing and mainten ance,

    ground-w a te r moni to r ing , and

    deed

    restr ict ions

    on future site

    use .

    Est ima ted Cost: S425.000

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    BeneficialReuse(RA-3)

    RA-3 invo lves

    a

    special PCB-

    handling approach

    to

    remove

    s ludgew i th

    PCB concentrat ions

    at

    or

    above

    50 ppm and

    recycle

    th e

    s ludge

    for

    agricu l tura l use.

    Estimated

    Cost:

    8.8 M ill io n

    In-PlaceCapping

    (RA-4)

    RA-4 inv olve s dike construc-

    tionto

    isolate

    and

    consolidate

    sludge containing PCB concen-

    trations

    at or

    above

    50

    ppm.

    Lagoon

    areasnot

    already cov-

    ered by natural vegetation

    w o u l d then be covered with soil

    and

    seeded. This alternative

    alsoinclude s moni tor ingand

    maintenance activit iesand

    future

    deed restrictions. U.S.

    EPA

    recommends RA-4

    because itprovidesth e best bal-

    ance

    w i t h

    respect to the nine

    evaluation criteria (see Figure

    2) .

    Est imated Cost: 1.8

    M i l l i on

    In-Situ

    Solidification/

    Stabilization (RA-5)

    R A 5

    invo lvesd ike const ruc-

    t ion

    to isolatean dconso l ida te

    s ludge

    con ta in ing

    PCBconcen-

    t ra t ionsat or

    above

    50

    p p m .

    R A 5

    also

    i n v o l v e s

    in -p lace

    s ludge t rea tment

    and

    c o n t i n u a -

    t ion

    of i ns t i t u t i ona l con t ro l s as

    descr ibed inR A - 2 .

    E s t i m a t e d Cost : S23-S28

    M i l l i o n

    Ex-SituBiological

    Treatment

    -

    Reuse Residue

    (RA-6[a])

    RA-6a inv olv es removal and

    biological treatment of lagoon

    s ludge w i th

    PCB

    concentrations

    ator

    above

    50ppm. Treated

    sludge

    w ou ld

    be

    recycled

    fo r

    agricultural use.

    Estimated Cost:

    $44-$66

    Mil l i on

    Ex-Situ

    Biological

    Treatment

    -

    Landfill Residue(RA-6[b])

    RA-6b is similar to RA-6a,

    except treated sludge would

    be

    disposed

    of in a

    Wiscons in solid

    was te

    landf i l l

    rather thanbe

    recycled.

    Estimated Cost:

    $64-$89

    Mil l ion

    Ex-Situ ChemicalTreatment-

    Landfi l l Residue (RA-7)

    R A 7

    invol ves removal and

    chemical t re atm ent of lagoon

    s ludge

    w i th

    PCB

    concentrat ions

    at or

    above

    50

    ppm . Treated

    s ludgew o u ldbe disposed of in

    a

    solid

    was t e landf i l l .

    Estimated Cost:$58-$73

    M i l l i o n

    TSCA Landf i l lDisposal( R A -

    8)

    R A 8

    i n v o l v e s

    r em ov a l

    andsta-

    b i l i za t i o n of

    s lu d g e

    c o n t a in in g

    PCBc o n c e n t r a t i o n s at or

    a b o v e

    50 p p m .fo l lowed by d i sposa l of

    the s t ab i l i zed

    s l u d g e

    in a

    T S C A - p o r m i t t e d

    l a n d f i l l .

    E s t i m a t e d Cost

    S I 6 0 - 5 1 6 8

    M i l l i o n

    4

    WisconsinSolidWaste

    Landfill

    Disposal( R A - 9 )

    RA-9 i nvolve s removal

    and

    sta-

    bi l izat ionof s ludge conta in ing

    PCB

    concentrations

    at or

    above

    50

    ppm, fol lowed

    by

    disposal

    of

    the stabil ized sludge in a

    Wiscons insolid waste landfi l l .

    Es t imated

    Cost:

    $40-$53

    Mil l ion

    U.S.EPA

    Recommendation

    U.S. EPA recommends In-

    Place Capping (RA-4).

    RA-4 would protect human

    health

    and the

    environment,

    beeasy to implement, com-

    pl y

    w ith state

    and

    federal

    regulations,

    reduce move-

    ment

    of

    contaminants ,

    an d

    becost

    effective.

    The

    Next Step

    Before se lec t inga finalc l e a n u p

    p l a n ,

    U . S .EPA

    w i l l cons ider

    com m en t s

    rece iv edd u r i n ga

    30-day p u b l i c

    c o m m e n t p e ri o d

    from N o v e m b e r18

    th rough

    December 18, 1996. The

    c l e a n u p p lan wi l l be

    descr ibed

    i n a f i n a l dec is ion document ,

    ca l l ed

    a

    record

    of

    dec i s ion ,

    w h i c h

    w i l l

    be ava i l ab l e fo r

    p u b l i c rev iew in ear ly

    1997.

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    PublicCommentSheet

    Your input

    on U.S. EPA's Proposed Planfor the Madison M etro

    Super fund site

    is impor tan t . Pub l ic comments

    assist U.S. EPA in

    selecting

    its finalcleanup p lan.

    Y oum ay use the

    space

    below to

    write your comments about U.S. EPA'sProposed Plan. Com ments must

    be

    postmarked byDecember 18 , 1996. If you hav e questions abo ut th e comment period, contact Susan Pastor at

    312-353-1325 or

    1-800-621-8431.

    Thosew ith e lec tronic com mun icat ions capabi l i t iesm ay submit their com -

    men ts to U.S. EPA via In ternet to: pas tor .susan@ epamail .epa .gov

    N a m e :

    Address:

    C i t y :

    Sta te :

    Z i p : _

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    Madison Metro Superfund Site

    Public

    Comment Sheet

    Fold

    on

    Dashed Lines, Staple.

    Stamp,andMail

    N a m e _

    A d d r e s s ^

    Ci ty

    Z ip

    St a l e

    Place

    Stamp

    Here

    Susan

    Pas tor ( P - 1 9 J )

    C o m m u n i t y I n v o l v e m e n t

    Coord ina tor

    Office of Publ i c Af fa i r s

    U.S.

    EPA . Re g i on

    5

    77

    Wes t J ackson Boul eva rd

    Chicago . 1L60604

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    Evaluation

    able

    Figure2

    EvaluationCriteria

    Remedial Remedial Remedial Remedial Remedial Remedial Remedial Remedial Remedial Remedial

    Alternative Alternative Alternative Alternative Alternative Alternative Alternat ive Alternative Alternative Alternative

    1

    2 3 4 5

    6(a)

    b ) 7 8 9

    No

    Action

    1 . Overal l Protection of

    Health

    &

    Envi ronment

    2.Compl iance wi th AR AR s

    3

    Long

    Term

    Effect iveness

    and

    Permanence

    4.

    Reduct ion

    ofTowci ty. Mobihty .

    or

    Volume

    through

    Treatment

    5. Short-Term Effectiveness

    6.

    Implcmentabi l i ty

    7. Cost

    8.

    Support

    Agency Acceptance

    9.Commu n i tyAcceptance

    D

    D

    D D

    NA

    $0 $425,000

    8.8

    $1.8

    23-28

    $44-66

    S64-89

    58-73 160-168

    $40-53

    M i l l i o n Million M i l l i o n M i l l i o n M i l l i o n

    M i l l i o n

    M i l l i o n M i l l i o n

    The

    Wisconsin Department

    of

    NaturalResourcesacceptsU.S. EPA's recommended alter native

    C o m m u n i t y

    acceptance

    of therecommended alternative

    w i l l

    beevaluated afterthepublic comment

    period.

    |

    Fullymeets criteria **'

    Partially

    meets

    criteria | |Does

    ot

    meet c riteria

    NA-Not Applicable

    Evaluation

    Criteria

    U.S.

    EPA

    used

    the

    fo l l ow i n g

    nine criteria

    to

    evaluate each

    alter-

    nat ive. The

    Evalua t ion

    Table (Figure2)compares th e alterna-

    t ives to

    these criteria.

    Overall

    Protection

    of Human

    Health

    and the

    'Environmentdetermines whetheranalternative eliminates,

    reduces,

    or

    controls threats

    to

    public

    healthand the

    environment

    th rough

    ins t i tu t iona l

    controls, engineering controls,o rtreat-

    ment .

    2. Compliancewith Applicableor Relevantand

    Appropriate Requirements (ARARs)

    ev a l u a t es wh e th e r

    th e

    a l t e rn a t i v e

    meetsfederal and

    state env i r o nm en t a l statu tes ,

    regu-

    l a t ions , and

    otherrequ i r emen t s

    that pertain to the s i te or

    w he t he r

    aw a i v e ris

    justified.

    3. Long-TermEffectiveness and Permanenceconsidersthe

    ab i l i ty of an

    al te rna t ive

    tom a i n t a i n

    protection

    of

    h u m a n

    health

    and the e n v i r o n m e n t ov er

    t i m e

    and the

    r e l i a b i l i t y

    of suchpro-

    t ec t ion .

    4. Reduction of Contaminant Toxicity, Mobility,or Volume

    Through Treatment

    e v a l u a t e s

    a n

    a l t e r n a t i v e ' s

    use of t re a tme n t

    to

    reduce

    the

    ha rmfu l effec ts

    of

    pr i nc i pa l

    c o n t a m i n a n t s ,

    t h e i r

    ab i l i t y

    to mo ve in the

    e n v i r o n m e n t ,

    and the

    a m o u n t

    of

    contami-

    na t io n presen t .

    5. Short-Term

    Effectiveness considers

    thelengthoftime need-

    ed to

    implement

    an

    alternative

    and the risks the

    alternativeposes

    to

    workers, residents,

    and thee n v i r o n m e n t

    during

    i m p l e m e n t a -

    tion.

    6.

    Implementabilityconsiders

    the

    technical

    and

    administrative

    feasibi l i ty of imp lemen t i ng th ealternative, suchasrelative avail-

    abil i tyof

    goods

    and

    services.

    7. Costincludes estimated capitalandoperationandmainte-

    nancecosts,as

    w e l l

    aspresent worth costs. Present worthcostis

    th etotal cost of an al ternat iveover t ime intermsoftoday' s dol-

    lars.

    8.

    State

    Acceptance considersw h e t h e rt hestate agrees w i t h

    U.S.EPA's an a l y ses and r e c o m m e n d a t i o n sof theRI/FSand the

    Proposed P lan .

    9. Community Acceptance

    w i l l

    beaddressed in theROD.

    C o m m u n i t y acceptanceof therecommendedc lean up ac t ion w i l l

    b e

    e v a l u a t e d af te r

    th e p u b l i c

    co mment pe r i o d

    and before the

    record oi d e c i s i o n i s

    i s sued .

    P u b l i c

    c o m m e n t s

    and U.S.EP A

    responses to thosec o m m e n t s w i l l b e presen ted in the resp on s i v e -

    nes - , summarx .

    w h i c h w i l l he a t t a ch ed to the recordo f

    d e c i s i o n .

  • 8/11/2019 PROPOSED PLAN Madison Metropolitan Sewerage District Superfund Site

    8/8

    Additional Information

    Ifyouhave questions abouttheinformationinthisfactsheetorwould like additional information aboutthe

    Madison Metro Proposed Plan, please writeorcalltheind iv idua lslisted below.

    U.S.

    EPA

    Contacts

    State of

    Wisconsin Contacts

    SusanPastor(P-19J)

    Community Involvement

    Coordinator

    (312)353-1325

    BobWhippo (SR-6J)

    Remedial

    Project

    Manager

    (312)886-4759

    Toll-Free:

    1-800-621-8431

    U.S.EnvironmentalProtection

    Agency

    77

    West Jackson Boulevard

    Chicago, Illinois 60604

    Larry Lester

    StateProject

    Manager

    (608)

    266-7596

    Wisconsin Department of Natural

    Resources

    Bureau

    o fSolida ndHazardous Waste

    P.O. Box7921

    Madison,Wisconsin 53707

    Chuck Warzecha

    Hydrogeologist

    Wisconsin DMsionofHealth

    1414E.

    Washington, Room

    96

    Madison,W I 53703-3044

    (608)

    267-3732

    Th eProposedPlan,

    Community

    Involvement Plan,

    fact

    sheets,and othersite-related information areavail-

    able

    forreviewin thesite information repositories at theMadison Public Library,201West Mifflin

    Street,Madison,

    and the

    Madison Metropolitan Sewerage District, 1610Moorland

    Road,

    Madison.

    An

    Administrative Record file,w hichcontainsthe information upon

    w hich

    theselectionof thecleanup plan

    will

    be

    based,

    hasalsobeen established at the

    Madison Public Library.

    EPA

    Office of

    Public

    Affairs(P-19J)

    U.S.

    EPA

    Region

    5

    77WestJackson Boulevard

    Chicago,

    Illinois

    60604

    Bob

    Whippo SR-6J)

    USEPA

    77W. Jackson B lvd.

    Chicago, IL6 6 4


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