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    DESIGN CONSTRUCTION

    AND

    MANTENANCE

    OF

    RECHARGE

    BASINS

    GEOTECI   INCAL

    DESIGN

    PROCEDURE

    C- r DP- 8

    e vi s i o n 4

    GEOTECHMCALENGNEERNG

    BUREAU

    APRIL 2 7

    I F

    NEWYORKSTATE

    DEPARTMENTOF

    TRANSPORTATION

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    GEOTECHNCAL

    DESIGN

    PROCEDURE 

    DESIGN CONSTRUCTION

    ANDMAINTENANCE

    OF

    RECHARGEBASINS

    GDP-8

    evi si on 9

    STATEOF

    NEW

    YORK

    DEPARTMENTOFTRANSPORTATION

    GEOTECHNCAL

    ENGNEERNG

    BUREAU

    APR L2007

    EB07-039

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    PREF CE

    Thi s manual

    i s

    i nt ended t o serve as a gui de f o r det er mni ng

    f e a s i b i l i t y ,

    de s i gn ,

    c on s t r u c t i o n, and

    mai nt enance

    r equi r ement s f o r r echar ge b a s f v s ( mor e pr e c i s e l y

    b as i n s As

    a user s

    manual ,

    d i s c us s i o ns

    of

    t h e or e t i c al o r

    devel opment al

    aspect s a r e

    avoi ded

    s i n ce t h e s e s ub j e c t

    ar eas

    have been

    document ed pr evi ousl y by t h e Depar t ment

    The manual has been devel oped

    such t h a t d es i g ne r -

    users

    need

    n o t

    be s o i l e x p e r t s ,

    al t hough appr opr i at e i n pu t

    f r o mt h i s e xpe r t i s e

    i s

    of pr i me i mpor t ance  

    t i s expect ed

    t h a t t h i s

    manual , w t h

    t h e i ncl uded

    comput er pr ogr amRECHARGE

    wi l l

    enabl e t h e

    pr acti ci ng engi neer t o desi gn b as i n s e a s i l y

    and

    qui ckl y   pr ogr amRECH RGEdi s k et t e f o r use on

    an

    I BMPC-AT X7

    PS/ 2 or

    any I BMcompat i bl e i s

    a l s o av ai l ab l e

    upon

    wr i t t en

    r equest

    t o :

    Di r ect or

    Ge ot e c l u i i c al

    Engi neer i ng

    Bur eau

    NewYor k S t a t e

    Depar t ment of Transpor t at i on

    50 Wol f

    Road,

    Mai l

    Pod

    31

    Al bany, NewYork

    12232

    Whi l e r e p l e ni s l n ne nt

    of

    gr oundwat er t hr ough r echar ge has

    been

    pr oven t o be t e c hn i c a l l y f e a s i b l e and

    c os t e f f e ct i ve ,

    t h i s Bur eau b e l i e ve s t h a t t h e success

    of

    any r echar ge p r o j e c t depends upon

    adher ence

    t o t h e p r i n c i p l e s pr esent ed i n t h i s manual   Fur t her mor e,

    peri odi c

    r evi ews of basi n

    per f ormance

    need

    t o be an ongoi ng a c t i v i t y   I nf or mat i on obt ai ned f r o m

    t h e s e

    r e - v i e ws

    can

    pr ovi de t h e Depar t ment w t h

    a g r e a t e r exper i ence base   t i s t h e r e f o r e r ecommended t h a t

    each

    Regi on

    e s t ab l i s h

    an

    i nvent or y

    of

    r echar ge basi ns whi ch have

    been

    desi gned i n accordance w t h t h i s

    manual

      Thi s i nvent or y shoul d be

    r evi ewed

    on a

    schedul ed b as i s

    t o eval uat e

    per f or mance and

    gai n

    f u r t h e r

    exper i ence   I n i t i a l

    and

    updat ed

    i nvent or y

    i nf or mat i on

    shoul d

    be

    transmtted t o

    t h i s

    Bur eau wher e a mast er

    f i l e

    wi l l be

    mai nt ai ned

     

    EB07-039 Page 2 of 28

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    T BLEOFCONTENTS

    PREFACE   2

    TABLEOF

    CONTENTS

    3

    LI STOFFI GURES   5

    LI STOFTABLES 6

    LI ST

    OF NOTATI ONS  

    7

    1  

    I NTRODUCTION

      8

    1

      1 Recharge : Backgr ound

    and

    Per specti ves

     

    8

    1   2

    A r t i f i c i a l l y

    I nduced

    I n f i l t r a t i o n

    of

    St oi nnwater

    An Al t e r n at i v e 9

    1

      3

    Hydr aul i cs

    of

    n f i l t r a t i o n

    and Rechar ge

    9

    2   DESI GNPROCEDURE 11

    2   1 Gener al  

    l l

    2   2

    Ar ea Reconnai ssance

    11

    2   2   1 Basi n

    conf i gur at i on

    and

    S i t e

    Pl anni l g   13

    2   3 Wat er shed

    Hydr aul i cs

      14

    2   3

      1 Desi gn

    StromS el ec t i o n 14

    2   3 2

    Det erm nat i on

    of Mass I nf l ow Cur ve 14

    2   4

    Subsur f ace S o i l s

    Expl orati on   15

    2

      5 S o i l Propert i es

    and Labor at or y Tests Requi r ed

    f o r Anal ysi s 15

    2

      6

    S o i l

    Desi gn

    Anal ysi s 16

    2

      6

      1

    S o i l

    P r o f i l e Eval uat i on 16

    2

      6 2

    Det erm nat i on

    of S o i l Desi gn

    Par amet ers   16

    2

      6

      3

    The I n f i l t r a t i o n

    Equat i on

     

    19

    2

      6 4

    Basi n Oper at i ng

    Head

    and Bas i l

    Top

    Sur f ace Ar ea

    2

    2   7 Basi n

    Si ze

    Desi gn 20

    2

      7

      1 Comput er Pr ogr am

    RECH RGE

    20

    3  

    CONSTRUCTI ON

    GU DELINES

    22

    3   1

    Const r uct i on

      22

    3   2 Wat er shed Erosi on Cont r ol   22

    3

      3

    I n l e t

    Desi gn

    23

    3

      4

    Turf

    Es t a bl i s ht n en t  

    23

    3   4   1 Topsoi l   23

    3   4 2 F e r t i l i z a t i o n 23

    3   4 3

    Seedi ng

    23

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    4 X I : AI NTEN- NI CE . 24

    4 . 1

    Gener al

      . 24

    4 . 2 Basi n Per f or mance Decl i ne  

    24

    4 . 3 Turf a s a Pr event i ve of

    Decl i ne

    24

    4 . 4 I nspecti on

    and Tr oubl eshoot i ng

      . 2 5

    REFERENCES   . 27

    APPEND C ES . 25

    Exampl e

    Pr obl ems

    Manual

    Comput at i on

    US

    Cust omar y Uni t s ) A- 1

    Exampl e Pr obl ems

    Manual

    Comput at i on

    I nt e r n at i o na l Syst em

    of Uni t s ) A- 12

    B  ProgramRECH RGE Sequence of Oper at i on

    I nput

    Dat a Sequence

    Out put Sequence and Error

    Messages

    B- 1

    C

      Exampl e Pr obl em  Comput er

    US

    Cust omar y Uni t s ) C- 1

    Exampl e Pr obl em

     

    Comput er

    I nt e r n at i o na l Syst em

    of

    Uni t s ) C- 10

    D  Program

    RECH RGE

    L i s t i n g

    US

    Cust omar y Uni t s ) D- 1

    Program

    RECH RGEL i s t i n g I nt e r n at i o na l

    Syst emof

    Un i t s )

    . D- 37

    E

     

    Sel ected Rai nf al l

    I n t e n s i t y , Fr equency and

    Dur at i on

    Curves f o r t he S t a t e

    of

    NewYor k E- 1

    EB07 039 Page4 of 28

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    LISTOFFI GURES

    Gr oundwat er Re pl e r u s hn i e nt

    Through a

    Rechar ge

    Ba s i n 10

    2   Sequence of Steps hi

    Desi gn Procedur e

    12

    3   S o i l Porosi ty i n Rel at i on t o Gr ai n s i z e

    C l a s s i f i c a t i o n

    18

    4  

    Capi l l ary

    Suct i on

    P ot e nt i a l TermW  v s  

    Gr ai n

    Si ze of

    Co l i e si o nl es s S o i l s 18

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    SYMBOL

    DESCRIPTION

    LIST

    OFNOT TIONS

    EB07 039 Page of 28

    Hor i zont al Pl ane Ar ea of t h e Basi n a t Dept h of

    H 2

    A Basi n Top S u r f a c e , Ar ea

    G S p e c i f i c Gr avi t y

    of S o i l

    S ol i ds

    H Maxi mumBasi n Oper at i ngHead

    ks

    C o e f f i c i e n t

    of

    Saturated Per meabi l i t y

    k c

    Hydr aul i c Conducti vi t y

    of

    Tr ansm ssi on Z o ne ,

    7

    S o i l

    Por osi t y

    Q Cumul at i ve h i f i l t r a t i o n

    Fl ow

    Cumul at i ve I nf l ow

    s

    Degr ee o f Sat ur at i on

    SS S p e c i f i c Surface of S o i l s

    t Ti me

    w

    n

    Natural Dr ai ned Moi st ur e Cont ent

    A

    n

    Vol umetr i c Wat er Cont ent i n Natural Dr ai ned

    S t a t e ,

    Vol umetr i c

    Wat er

    Cont ent i n Tr ansm ssi on Zone

    a

    Hvdi

    aul i c D i i t s i v i t y

    Capi l l ar y Suct i on P o t e n t i a l a t Natural Dr ai ned Moi st ure Cont ent

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    Unsaturat ed

    So i l

    Laver s)

    t

    l

    H=Peak Operat i ngHead

    Recharge

    Basi n

    Groundwater Tabl e

    Wet t ed

    Front of

    Unsaturat ed

    Fl ow

    a s

    a

    Funct i on of Ti me

    Fi gur e Gr om dwat er

    Repl el usl uuent

    t hrough

    a

    Recharge Basi n

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    2

     

    DESI GNPROCEDURE

    2   1

    General

    The

    desi gn o bi e ct i v e i s t o s a f e l y di spose of s t o rmrunoff as unobt r usi vel y

    and

    i nexpensi vel y as

    poss i bl e

     

    Thi s

    i s

    b e s t

    achi eved,

    wher e

    p o s s i b l e ,

    by

    a di str i buted

    approach,

    i

    . e

     

    di spose

    of

    g r a t e r

    a t s e l e c t e d depressi ons al ong t h e e n t i r e

    p r o j e c t

    l e n g t h   Conver sel y, t he p r a c t i c e of

    c o l l e c t i n g

    p r o j e c t

    runof f f r o mmany square

    ml es and

    d i r e c t i n g

    t

    t o

    a

    s i n gl e di schar ge

    po i n t o f f er

    provi des

    a

    r e s u l t t h a t

    i s moreexpensi ve  di s r u pt i v e

    t o c on s t r u ct ,

    and

    poss i bl y

    c o s t l y

    t o

    mai nt ai n  

    The desi gn of a r echarge basi n

    c on s i s t s of a

    number

    of di s c r et e s t e p s , as

    shown

    i n

    Fi gur e 2   Each

    s t e p

    i s

    referenced

    t o

    a s e ct i o n

    of

    hi s chapter

    wher e

    i t i s

    di scussed i n

    de t a i l  

    Basi n

    recharge

    i s

    f e a s i b l e

    wher ever t h e f o l l ow ng condi t i ons

    ex i s t

    :

    1   The

    s o i l s ,

    excl udi ng the t op 5 f t  

    1

     

    5 m of surface

    s o i l a r e r e l a t i v e l y

    p e t

    meabl e,

    2   Unsaturated condi t i ons

    e x i s t

    t o a

    consi der abl e

    depth bel owt h e surface   I i i f

    l t r a t i o n

    cannot occur i f a s o i l i s al r eady s a t u r a t e d

    by

    per manent gr oundwat er   For a desi gn t o be

    v a l i d , a good

    r ul e- of- t humb

    i s

    t h a t

    t h e dept h

    of

    unsaturated s o i l bel owt h e proposed bash]

    f l o o r i s g r e a t e r t han 25 percent of t h e

    peak

    basi n operati ng

    head

      The

    peak

    basi n

    operati ng head, H, i s def i ned as t h e

    maximum

    dept h of water perm ssi bl e f o r t h e

    proposed b a s i n ,

    3   Unsaturated s o i l s a r e not l a t e r a l l y c on f i n ed,

    i

      e   they have t h e capaci t y f o r wat er t o move

    and

    s t o r e h o r i z o n t a l l y ,

    and

    4

     

    S u f f i c i e n t space

    i s

    a va i l a bl e f o r

    s i t t i n g s i n g l e

    or

    mul t i pl e

    basi ns

    i n

    t h e

    p r o j e c t

    v i c i n i t y  

    Maximum

    use shoul d be made of t h e surr oundi ng

    n at u r a l

    t e r r a i n , i nt erchange l oop

    i n t e r i o r s

    and o t h e r

    depressi ons  

    Su bs t a n t i a l

    runof f

    can

    be

    di sposed

    of by i n f i l t r a t i o n i n

    a

    vent smal l space  

    The r emai ni ng

    quest i on of

    recharge

    e f f i c i e n c y

    as r e l a t e d

    t o

    basi n

    s i z e

    can onl y be answer ed

    by

    appl yi ng t h e desi gn procedure  

    2

    . 2 Ar ea

    Reconnai ss ance

    Subsur f ace condi t i ons maybe

    gener al l y

    eval uat ed f o r recharge basi n f e a s i b i l i t y e a r l y i n p r o j e c t

    pl anni ng and w t hout bor i ngs through t h e use of t e r r a i n r econnai ssance

    t echni ques

      Thus

    i ncl udes

    compari son of a l t e r n at e basi n s i t e s al ong t h e

    proposed

    al i gnment s   Ref erences

    used

    i n t h us phase

    may ncl ude o l d b or i n gs , a e r i a l photographs,

    wel l

    r e c o r d s , gr oundwat er

    b u l l e t i n s ,

    geol ogi c

    r e p o r t s , a g r i c u l t u r a l s o i l survey reaps and

    b u l l e t i n s , constr ucti on

    records

    of

    excavati ons

    i n

    t h e

    a r e a ,

    and t h e

    Depar t ment ' s

    s o i l survey r e p o r t s , i f a vai l ab l e, f o r t he p r o j e ct area  hn f o r i n at i o n

    f r o m

    t h e s e

    sources

    combi ned

    w t h

    f i e l d i n s pec t i o t L s wi l l

    gi ve

    good

    i n si ght i n t o

    t h e

    p o t e n t i a l

    of

    recharge basi ns

    f r o m

    t h e st andpoi nt

    of

    f avorabl e subsur f ace condi t i ons   Thus research e x er c i s e

    may e l i m n a t e muchwork other w se necessar y t o di s c l o s e t h e gener al f e a s i b i l i t y of basi n desi gns

    a t

    gi ven l o c a t i o n s  

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    2   6   1 Soi l P r of i l e

    Eval uat i on

    7 Basi n Si ze Desi gn

    E 07 039 Page 1   of 8

    Figure2 Sequenceof Steps i n

    Desi gn

    Procedure

    6   2

    Det er m nati on

    of Soi l

    Desi gnParameters

    2

    Area

    Reconnaissance

    2   1 Basi n Conf i gur at i on

    and S i te

    Pl anni ng

    2   3   1

    Desi gnStorm

    Sel ecti on 4

    Subsurface

    Soi l s

    Expl orati on

    StormDr ai n Desi gn 5 Laborat ory Test i ng

    2   3   2 Mass I nf l ow 6 Soi l

    Desi gn Anal ysi s

    Det er m nati on

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      2

    . 1 Basi n

    Conf i gur at i on and S i t e Pl anni nl g

    Al l l ocat i ons

    f avor abl e

    for basi ns i n

    t er ms

    of

    o i l s ,

    groundwat er

    dept h

    andt opography

    shoul d be del i neat ed  f i t t h i s

    t i me,

    t he

    desi gner

    shoul d s t r i v e for opti mumr e s u l t s for

    hydr aul i c

    per f ormance,

    const r uct i on

    f e a s i b i l i t y

     

    envi r onment al

    e s t h e t i c s , c o s t andmni mum

    f turemai nt enance r equi r ement s   These i deal s canbe best approached by subdi vi di ng t he

    t o t a l proj ect wat er shed

    area

    i n t o smal l er uni t s i f possi bl e  

    Each

    woul dbe ser ved by i t s own

    smal l , l e s s conspi cuous recharge basi n whi chwoul dappear

    more

    or l e s s l i k e a

    depr essi on

    rather

    t han

    some

    ki nd of

    unsi ght l y wor ks I n t i e s sense, t he desi gner i s

    more

    cl osel y

    si nn. n l a t i n g the nat ural r echar ge process  

    Theopposi t e approach

    of

    usi ng

    a

    si ngl e

    or very smal l

    number

    of

    basi n

    s i t e s

    l eads t o l arger

    r unof f vol umes

      Thi s

    r equi r es

    greater basi n dept hs, and

    usual l y

    steeper si de sl opes because

    of

    l imt s i n

    t he s i z e of the

    area avai l abl e,

    not

    t o ment i on

    l onger and

    l arger pi pe

    nuns

     

    Where choi ces

    ar e avai l abl e, t he desi gner' s

    approach

    shoul d be i nf l uencedby

    t he

    f ol l ow ng

    characteri sti cs of

    basi n perf or mance :

    Whi l e l ar ge operat i ng dept hs wi l l i n f i l t r a t e

    more water

    f a s t e r t han shal l owdept hs, the

    f ol l ow ng di sadvant ages are

    i ncurr ed

    :

    a  

    Essent i al

    dr yi ng out of the f l oor a f t e r astori n i s i mpededby restri cted exposure t o

    wnds andsunl i ght   That i n turn causes mcrobi al growt hs t o

    rapi dl y

    popul ate the

    s o i l at the f l oor

    sur f ace

    andcl og t he por es ( see Sec   4 . 2 Thi s adver sel y affects t he

    a b i l i t y

    of l oor turf and grasses t o assi ml at e

    norms i l t i n g

    ( see Sec   4 3 The effects

    are

    more

    pronounced as basi ns become deeper , maki ng i t

    more

    d i f f i c u l t for the

    basi n

    t o be sel f =nnmt ai ned 

    b

      Deepbasi ns requi r e protecti on for peopl e

    and

    cars   They al so r equi r e substant i al

    f enci ng

    t o keep out trash

    or

    r efuse dumpi ng  

    c

     

    echar ge basi n

    f unct i ons

    onl y t emporar i l y

    and

    duri ng

    i nf r equent

    r a i n f a l l

    peri ods

     

    Consequent l y,

    i t

    makes i t t l e sense f or t he

    area occupi ed

    by

    a desi gned depr essi on

    t o

    be unsui t abl e

    and

    cat egori cal l y deni ed

    for other

    uses

    at other

    turns

      Conver sel y,

    t he

    potent i al exi sts for awel l

    desi gned

    basi n t o be i nt egrat ed i n t o

    a

    pl easi ng sceni c par t

    of the

    r oadsi de

    l andscape, a

    l ocal

    pl ayi ng f i e l d ,

    etc 

    The

    desi gn method wi l l provi de a recharge

    basi n

    that wi l l not overf l owfor t he i nci dence

    of

    storm

    equal

    t o

    the desi gn

    storm  Sooner or

    l a t e r , a

    stormw l l occur

    and

    cause

    overf l owof anyr easonabl y

    si zed basi n  

    Sucha

    storm

    magni t ude woul dprobabl y cause

    w de- scal e

    f ol di ng no

    matt er what

    provi si ons

    weremade for storm~7ater di sposal  

    Ther ef or e,

    the

    desi gner

    shoul d choose a c o n s e t - \ 7 a t i x - e d e s i g t l storm

    such

    that basi n

    overf l owwi l l not occur w t hout

    general f l oodi ng

    of dr ai nage systemel sewher e i n the

    l o c a l i t y

     

    The desi gner

    must

    under st and t h a t most

    f i i t u r e

    basi n mai nt enance, r econst ruct i on or

    r emedi al t r eat ment s maybe kept t o amni mumi f careful s i t e pl anni ng i s per f or med

    bef ore detai l ed desi gn  _ A s detai l ed desi gn advances for t he di str i but ed

    smal l

    basi ns,

    EB07 039 Page 3 of 8

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    some compr omses

    may

    be necessar y because of

    r e s t r i c t e d ri ght - of - way

    or o t h e r

    condi t i ons

    . Thus

    i s expect ed

    s i nc e

    compr om se i s not c ons i s t e nt wi t h r a t i o n a l engi neer i ng

    desi gn .

    2 . 3 Wat ershed Hydr aul i cs

    2 . 3

    . 1 Desi gn

    St or mSe l e c t i o n

    The o bj e c t i v e

    i n convent i onal drai nage

    desi gn i s

    t o

    obt ai n peak f l ow

    qua nt i t i e s

    per

    uni t

    t i me and

    v e l o c i t i e s f o r proper s i z i n g of var i ous el ement s i n t h e drai nage

    syst em

    .

    For

    basi n d ei gn, t h e cumul at i ve

    di scharge i n t o

    t h e basi l wi t h t i me i s

    t h e ohj e c t

    of

    n t e r e s t .

    However , when drai nage

    systemdesi gn i s

    compl eted, a l l

    f or mat i on necessar y t o

    c a l c ul a t e mass i nf l ow t o t h e

    basi n i s a va i l a bl e

    f o r use

    wi t h

    an

    appropr i at e

    desi gn Storm

    a s descr i bed i n

    t h e

    f ol l owi ng

    s e c t i on .

    Sel ect i on

    of

    r a i n f a l l

    i n t e n s i t y ,

    f r equency and

    durati on f o r

    a desi gn stormshoul d be

    made

    usi ng Weat her Bur eau d a t a

    pert ai ni ng t o

    t h e l o c a l i t y .

    Sel ect ed

    curves f o r New

    York

    S t a t e a r e

    shown

    i n

    Appendi x

    E

     

    The

    desi gn

    r a i n f a l l

    f r equency

    and

    durat i on

    t o

    be used

    i n

    const ructi ng

    t h e mass i l i t l ow curve

    of

    a i n f a l l shoul d be chosen

    wi t h

    due regard f o r

    po s s i b l e consequences

    of

    basi n over f l ow duri ng t h e

    peak of

    a s t o r m e s pe c i a l l y wher e

    t h at pa r t i c ul a r stormwoul d not

    be

    accompani ed

    by

    f l a s h f l oodi ng el sewhere i n t h e

    area

    .

    Local t opography, present or proj ect ed l and use

    and

    t h e adequacy of

    o t h e r

    storm

    drai nage syst ems i n t h e

    area

    a r e i mpor t ant consi derat i ons whendeci di ng

    on

    an

    adequat e ;

    y e t r e a s on abl e , recurrence i nt e r v al

    .

    I n ge ne r a l , under t h e condi t i ons t h a t a basi n over t

     

    l o -

      v

    woul d pond wat er on t h e hi ghway i n depressed s e c t i o n s , a 1 0 - or

    25- year storm

    woul d be

    adequat e and

    conservati ve

    .

    However , i f excessi ve basi n

    over f l owmay

    cause c o s t l y

    damage t o adj acent proper t y

    and d i s r u p t

    e s s e n t i a l a c t i v i t i e s , a

    50- yeas storm

    shoul d be

    chosen .

    2

    . 3 . 2 Det ermnat i on

    of

    Mass

    I nf l ow

    Cur ve

    The met hods used most

    t o

    devel op t he mass i nf l ow curve of runof f

    a t

    any gi ven

    r a i n f a l l

    f r equency a r e

    t h e r a t i ona l

    met hod and

    t h e u n i t hydrograph

    met hod .

    The r a t i o n a l

    met hod

    i s onl y

    r e l i abl e f or

    est i mat i ngpeak r u n o f f

    from

    drai nage areas

    l e s s

    t han 640 a c r e s

    ( 2 . 6

    f i n . Det ai l ed procedures

    used by t h i s

    met hod i n devel opi ng a mass i nf l ow curve e a r l be

    f ound i n Ref

    . 1 . Al t hough

    t h i s

    met hod

    i s

    mat hemat i cal l y s i mpl e , t h e

    desi gner

    must use

    j udgment

    i n

    eval uat i ng

    t he l i m t a t i o n s of t s accuracy .

    I n p a r t i c u l a r ,

    care must be exerci sed

    i n s e l e c t i ng t h e

    wei ght ed

    aver age runof f c o e f l l c i e n t ,

    s i ne

    i t can

    have

    a very

    s i g n i f i c a n t

    erect

    on

    t h e mass i nf l ow curve .

    For

    drai nage

    areas

    g r e a t e r

    t han

    64

    a c r e s

    ( 2

    . 6 1 c r n ) ,

    t h e uni t

    hydrograph

    met hod i s

    r ecommended

    f o r

    est i mat i ng runof f magni t udes

    of

    d i f f e r e n t

    f requenci es

    .

    To

    use t h i s

    appr oach

    . cont i nuous records of runof f and p r e c i p i t a t i o n f o r t h e pa r t i c ul a r drai nage area

    a r e

    needed .

    E 07-039 Page

    1

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     number

    of

    o t h e r met hods

    have been devel oped

    f o r

    represent i ng

    a u n i t hydrograph i n

    term of runof f

    parameters such

    a s l a g

    t i me ,

    c o e f f i c i e n t of peak di scharge, t i me

    c o nc e nt r a t i o n,

    storage

    c o e f f i c i e n t ,

    et c . I f

    such

    parameters c a l l be adequat el y r e l a t e d t o

    measurabl e

    physi cal

    c ha r ac t e r i s t i c s

    of water s h e ds , i t becomes po s s i bl e t o synthesi ze uni t

    hydrographs f o r ungaged

    watersheds

    .

    Three

    commonl y

    used

    t e c l n ni c l ue s

    f o r depi ct i ng

    uni t

    hydrogr

      aphs a r e t h e Cl ark, Snvder,

    and SCS

    met hods . Detai l s of

    each

    a r e general l y

    presented i n st andard

    hydrol ogy

    t e s t s ,

    `

    .

    Once

    a u n l i t hydrograph has been der i ved f o r a

    p a r t i c u l a r drai nage

    area

    and

    r a i n f a l l

    d ur a t i o n, t h e

    u n i t hydrograph

    and i nf l ow

    hydrograph

    f o r

    any

    other durat i on c a r s be obt ai ned  F i n a l l y , t h e i nf l ow

    hydrograph woul d

    be mat henl at c a l l s mani pul at ed

    t o

    y i e l d t h e

    mass

    i nf l ow curve

    .

    I f

    t h e wat ershed

    t r i but a r y t o

    t h e

    recharge

    basi n i s di vi ded

    i n t o subareas of homogeneous

    c h a r a c t e r i s t i c s , u n l i t

    hydrographs f o r each subareas a r e super i mposed

    t o r e s u l t i n

    a

    composi t e i nf l ow

    hydrograph

    f o r t he ent i r e wat ershed .

    2 . 4 SubsurTace S o i l s

    Expl orati ons

    Subsurf ace

    s o i l s expl orat i ons

    shoul d

    be

    schedul ed

    w th

    t he .

    Regi onal

    Geotechni cal

    Engi neer

    as

    soon

    as

    possi bl e

    a f t e r t h e

    proposed

    basi l s i t e s a r e e s t a bl i s h ed   Subsurf ace i nf ormat i on

    i s

    t hen

    a va i l a bl e at

    t i n e

    appropri ate

    t i me

    f o r desi gn use . These

    expl orat i ons

    a r e

    used

    f o r t he f ol l ow ng

    p i l l   poses :

    .

    To

    e st a bl i s h t h e subsurf ace s o i l p r o f i l e and l o ca t i o n of each unsat urated permeabl e s o i l

    l a y e r ,

    2 .

    To

    e st a bl i s h t h e hi ghest gr oundwat er

    and

    t h e

    perched

    water e l e v at i o ns ,

    and

    3 .

    To

    obtai n s o i l

    sampl es

    f o r l aboratory

    t e s t i ng

    t hroughout t h e p r o f i l e

    depths ,

    p a r t i c u l a r l y

    bel ow s i d e s l o pe s

    and

    t h e basi n

    f l o o r

    e l e v at i o n t o be e s t a bl i s h ed l a t e r .

    The

    number

    and

    e x t e n t

    of

    expl orat i ons f o r

    a

    s i t e

    wi l l

    be

    det erm ned

    by

    t h e

    Regi onal

    G e o t e c l n i l i c a l

    Engi neer ,

    based

    on

    t e r r a i n reconnai ssance d a t a ,

    i f a v a i l a b l e ,

    and ex i s t i ng

    knowl edge

    of

    o c al geol ogy and

    subsurf ace

    condi t i ons

    . However , at l e a s t

    one bori ng

    or

    t e s t

    p i t

    i s

    requi red f o r

    any

    s i t e t o

    provi de sampl es

    f o r

    t h e s pec i a l

    anal yses

    necessary

    t o cal cul ated

    t h e

    c h a r a c t e r i s t i c i n f i l t r a t i o n

    curve

     

    2

    . 5 S o i l

    P r o pe r t i e s and Laborat ory Tests Requi red

    f o r < - U l a l y s i s

    T i l e par t i c ul a r s t r a t a of

    n t e r e s t

    f o r

    d e t e r i n i i s i n g

    i n f i l t r a t i o n p r o pe r t i e s a r e t hose t h a t

    l i e

    d i r e c t l y

    bel owt h e basi l s i de s l o pe s and basi n f l o o r   Thi s shal l ow

    zone

    of s o i l ext endi ng

    f rom

    t h e

    gr ound

    surf ace

    t o

    a depth not exceedi ng 0. 25H

    f t

    .

    bel ow

    t h e basi n

    boor wi l l

    c o n t r o l

    a l l

    i n f i l t r t i o n

    out

    of

    t h e basi n

     

    I t

    does not mat t er whet her s o i l s f u r t h e r

    downhave

    g r e a t e r or l e s s e r permeabi l i t y, s o

    l ong

    as

    t hey

    a r e

    reasonabl y

    permeabl e t wo

    o r d e r s

    of

    magni t ude

    l e s s

    i s

    a

    reasonabl y

    l i m t ) ,

    a r e

    not

    l a t e r a l l y

    conf i ned and

    a r e

    unsat urated

     

    Because t h e

    basi n

    f l o o r e l e v at i o n

    i s

    not d e f i n i t e l y

    e s t a bl i s h ed

    u n t i l

    l a t e r , s o i l t e s t s a r e run t hroughout t h e depth of t h e expl orat i on t o accommodat e

    t h e range of possi bl e

    f l o o r e l e v at i o ns

    expect ed.

    NN here

    s o i l d ep os i t s a r e

    deep and

    uni f orm t h i s

    i s

    of

    i t t l e consequence and

    t h e

    t e s t i ng

    program

    can

    be abbrevi ated .

    EB07 039 Page 1

    5

    of

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    The e s t s

    r ecommended f o r

    c ohe s i o nl e s s ,

    no n- pl a s t i c s o i l s d i f f e r

    f rom

    t hose requi red

    f o r

    s o i l s

    e x h i b i t i n g

    p l a s t i c i t y ,

    as shown i n Tabl e 1   Tests

    a r e

    descri bed i n t h i s

    manual

    o r t l y byname  

    They

    may

    be perf ormed i n t he Regi onal S o i l s l aboratory o r

    by t h e

    Geot ecl mcal Engi neer i ng

    Bureau

    at

    t h e

    d i s c r e t i o n of t he

    Regi onal

    Geot echni cal

    Engi neer

     

    2 . 6 S o i l Des i gn

    _ a n a l y s i s

    2

    . 6 . 1

    E 07 039

    S o i l

    P r o f i l e Eval uat i on

    P l o t

    and summar i ze

    a l l subsur f ace

    and

    l aborat ory t e s t dat a   These dat a mus t be st udi ed

    w t h

    r e s p e ct t o t h e s o i l p r o p e r t i e s c o n t r o l l i n g i n f i l t r a t i o n at t h e s i t e   As

    a

    general r u l e , t h e

    c o n t r o l

    zone

    f o r

    t he

    i n f i l t r a t i o n r a t e wi l l

    be

    i n t he s o i l bel owt h e ba s i n s i d e s l o pe s

    and

    t h e

    i r s t

    0. 2>H f   of t he s o i l l a y e r under l yi ng t h e basi n

    f l o o r

      So i l p r o pe r t i e s out si de t h i s area

    may e x e r t

    a

    secondary c o n t r o l onl y

    when t h e s o i l

    l i s

    mar kedl y l e s s

    permeabl e and

    t h e

    p r o f i l e

    i s

    such t h a t l a t e r a l spread of t he wet t i ng f r o n t

    i s

    prevent ed i f i t s v e r t i c a l

    advance

    i s

    i mpeded

    by

    h i s

    l ay e r

     

    I n ot her words

    t h e surf ace c o n t r o l

    zone

    wher e t h e

    pri mary

    t ransmssi on

    zone

    i s

    e s t a b l i s h e d ,

    wi l l c o n t r o l

    i n f i l t r a t i o n under any

    condi t i on wher e t h e

    wat er t ransmt t ed

    t hrough i t

    has a pl ace t o

    g o ,

    v e r t i c a l l y and/ or

    l a t e r a l l y

     

    2 . 6 . 2 D e t e r i n i i n a t i o n of

    S o i l

    Des i gn Paramet ers

    The f ol l ow ng

    a d d i t i o n a l c a l c u l a t i o n s

    of s o i l

    pr o pe r t i e s a r e

    requi red f o r t h e

    i n f i l t r a t i o n

    a n a l y s i s

     

    a   Vol umet r i c wat er cont ent ui na t u r a l drai ned s t a t e , 0

    .

    The na t u r a l drai ned moi st ure cont ent of s o i l i s def i ned as

    t h e

    wat er hel d i n

    t h e

    s o i l a l t e r

    t h e

    excess g r a v i t a t i o n a l wat er has drai ned away

    and

    a f t e r t he r a t e of downward

    movement of wat er has p r a c t i c a l l y _ ceased   The vol umet r i c water cont ent i n na t u r a l

    drai ned

    s t a t e

    can be

    f ound f rom

     

    w-

    nG1 -

    i l

    wher e w r , = n a t u r a l

    drai ned moi st ure cont ent

    expressed as

    a deci mal

     

    Use 0

    . 03 f o r

    gravel s

    and

    s a n d s ,

    and 0

    . 05 f o r

    s i l t s

     

    G

      s p e c i f i c

    gravi t y of s oi l s ol i d s , and

    porosi t y  

    Page

    1 6 of 28

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    3

    Tabl e

    1

    Test Schedule

    The pur pose of t h i s anal ysi s i s t o est i mat e

    k

     

    based onk, - SS- qrel ati onshi p devel oped by

    Loudon

    .

    However, the anal ysi s s

    recommended

    onl y

    for

    sands and

    gr avel s

    havi ng not

    more

    than 5 ° passi ng the

    No

      200 (75

    htm si eve

      For

    materi al s

    havi ng

    morethan

    5

    f i d e s

    ski p

    t h i s anal ysi s anddet er m ne k  by l aborat or y t e s t  

    May

    be est i mat edf rom

    g r a i l s

    si ze

    descri pt i on

    as shown

    n

    Fi gur e 3 

    Esti mat edby Loudon Formula or maybe

    determ ned

    by

    l abor atoY

    .N  t e s t on s o i l

    sampl e,

    usi ng upward f l o w

     

    These t e s t s shoul d be per f or med onl y by t he Geotecl ni i cal Engi neer i ng Bureau at

    Al bany  

    y

    can

    be

    est i mat ed

    fromFi gur e

    4

     

    D {

    can

    be

    det er m ned

    from

    the

    si eve

    anal ysi s or

    hydr omet er t e s t

     

    EB07-039 Page 7 of 28

    Testi n

    a -

    ui r ed

    Test

    Property

    Symbol

    Cohesi onl ess

    Non- Pl ast i c

    Soi l s

    Soi l s

    Exhi bi t i ng

    Cohesi on

    O

    Pl ast i c i ty

    Speci f i c Sur f ace Anal ysi s SS Yes'

    No

    Natur al

    hi - Si tu Por osi ty Yes

    2

    Yes

    Speci f i c Gravi t y of S o i l

    Sol i ds

    Yes Yes

    Saturated Per meabi l i t y k

     

    No

    Yes`

    Capi l l ary Suct i on

    Potenti al

    Wn

    No

    YeS4

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      ' el l - Graded

    GRAVELS

    Gap-Graded

    GR4X L-5-A\D1I LZTI RES

    Fi ne Medi uui

    Medi umCoarse

    SAND1I LTTLRLS

    SANDSI LI

    MXTURES

    CLAY

    I I I

    0

    20

    0_255

    0

    30

    0. 35 0_40 0. 4

    ;

    0. 50

    NATURAL

    POROSITY

    Fi gure3 Soi l

    Porosi ty

    i n

    Rel at i on

    t o Grai nSi ze Cl assi f i cat i on (f rom

    Ref

      1)

    500

    100

    50

    10

    I I I

    I

    I 1

    11111

    1 1 1 1

    1101

    111111

    11 1111d

    1~

    1~010~

    J I I I~~~~

    1

    I I I I

    I

    I

    . I I

    I

    I 1

    I II i

    I

    111W

    I I

    I

    11111W

    II

    I I I

    1

    °,nkl 9 I

    ~~

    I~~

    ~

    I

    ~ ~~

    I

    I

    1

    1

    1 111 1

    1

    1 1

    ~1W 

    EB07039 Page18f 28

    100 0

    1

    0 5 0

    10

    005

     

    0

    GanSzemm

     010005

    001

    Fi gure4

    Capi l l ary

    Sucti onPotent i al

    Term

    xy   vs   Grai nSi ze of

    Cohesi onl ess Soi l s (f romRef   1)

    15. 0

    10. 0

    5. 0

    . 0

    0

     

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    b . Vol umet r i c water content i n t ransm ssi on

    zone

    dur i ng i f i l t r a t i o n , O

     

    Themoi st ure

    c o n t e n t

    i i l

    t h e t r ansmss i on

    zone

    dur i ng i n f i l t r a t i o n i s n o t

    k no , , v n

    bef orehand . However , moi st ure

    contents

    cor r espondi ng t o 80 and 70 s a t u r a t i o n

    can

    be assunned f o r s i l t s

    and

    s a nds ,

    r es pec t i v el y

    . Ther efor e,

    8 t

    can be f ound f r om 

    wher e s =

    degr ee

    of saturat i on expressed a s

    a

    deci nal ,

    and

    i l

    = p o r o s i t y .

    c .

    Hydr aul i c

    c o t n duc t i z %i t y

    of r a n s l i l i s s i o t l zone,

    k

     

    The

    hydr aul i c

    conducti vi t y

    of t he

    tr ansmssi on zone

    i s obt ai ned f r o m

    t he s a t u r a t ed

    s o i l permeabi l i t y,

    k  

    by means of

    he f ol l ow ng equat i on

    :

    wher e

    cumul at i ve

    i n f i l t r a t i o n

    f l ow

    a t

    any

    tune

    t ,

    yr n

    =

    c a p i l l a r y sucti on

    po t e nt i a l

    a t

    na t u r a l drai ned moi st ur e content p r i o r

    t o

    i n f i l t r a t i o n

    a = hydr aul i c d i f f  

    u s i v i t y

    H

    =

    maximumbasi n

    operati ng

    head, and

    Af=

    pl ane

    f l ow

    area whi ch i s

    defi ned a s t he ho r i z o nt a l pl an

    area of

    he basi n

    a t

    dept h

    of H/ 2  

    Eq

      ( 5 ) can

    al so

    be expressed i n t h e f o r m

    Q

    =

    N

    t ) /

    (6

    here

    N=

    2 k , ( H ' 2 +

    r c

    a ) ( 7 )

    EB07-039 Page 19 of 28

    k _ 5

    (O }

    On~

    ( 1

    -

    0 " )

    ( 3 )

    d . Hvdr auf c d i t f u u s i - \ - i t y ,

    a

    Thi s

    t e rm

    i s obt ai ned

    by

    t h e f ol l ow ng equat i on :

    =

    kt

    /

    ( Ot

      0

    )

    ( `

    2. 6 . 3

    The

    h i f l t r a t i o t i E c f u a t i o n

    The

    c ul nul a t i - - e

    i n f i l t r a t i o n

    quanti t y i s gi ve by :

    Q

    = 2k   ( I h2+ , ~+r ( t / na)

    ( 5 )

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    2 . 6 . 4 Basi n Oper at i ng Head and Basi n

    Top

    Sur f ace

    - A r e a

    For

    a

    gi ven unsaturated

    permeabl e

    s o i l subj ected t o i n f i l t r a t i o n , t h e c u r n t i l a t i v e

    i n f i l t r a t i o n f l o w,

    Q, t hrough s o i l at any t i me

    t

    i s a f uncti on o f the s o i l parameter s,

    t h e

    basi n oper ati ng

    head

    and pl ane

    f l ow

    area a s shown i n Eq

     

    5 . I f

    t h e

    basi l

    conf i gurat i on

    and s i d e

    s l o pe s a r e

    gi v en ,

    t h e

    pl ane

    f l ow

    area can be expressed i n t er ms of

    t h e

    basi n

    operati ng

    head, H, and cor r espondi ng basi n t op surf ace

    area

    .

    For exampl e,

    t h e

    pl ane

    f l ow

    a r e a ,

    -Af 

    f o r

    a square basi n

    w t h

    1 v e r t i c a l on2 hori zontal s i d e

    s l o pe s

    i s

    :

    A, = A, - 4

    H

    Y

    r

     ZV 4

    H

     

    wher e _ k= basi n t o p surf ace area

    Eq

      ( 5 ) i n di c at e s

    t h a t t h e i n f i l t r a t i o n quant i t y

    per u n i t of f l ow

    area

    i s d i r e c t l y

    pr opor t i onal

    t o

    the oper ati ng

    head

    s e l e ct e d

    .

    S i m l a r l y ,

    i f

    the

    maxi mum

    operat i ng

    head

    i s

    kept c o n s t a n t , t he f l ow

    mas s i n f i l t r a t i o n quant i t y

    i s d i r e c t l y

    pr opor t i onal t o t h e

    f l ow area  

    The

    d es i gn er , t h e r e f o r e ,

    can

    e s t a bl i s h

    a

    whol e

    spectrum

    of

    pai r ed val ues

    f o r

    H

    and

    o r

    t

    t h a t wi l l provi de an equal hydr aul i c r e s u l t

    f o r

    a pr oposed basi n

    .

    Thus becomes a

    r e l a t i v e l y si mpl e t a s k usi ng

    t h e

    comput er

    program

     

    These r e s u l t s can t hen be

    exam ned

    w t h var yi ng shapes and s i d e

    s l o pe s

    t o f i n d a

    b e s t

    mat ch f o r a s i t e

    The

    o b j e c t i v e , of

    c o u r s e ,

    i s t o f u nd an

    opti mumpai r

    of

    v al u e s ,

    Hand

    A, ;

    f o r t h e

    s i t e i n t erms of envi r onment al i mpact,

    a v a i l a b l e ri ght - of - way

    and a

    l o n g ,

    mai ntenance- f  

    e e

    l i f e .

    2 . 7 Basi n Si z e De s i g i m

    Rat i onal basi n desi gns

    can

    be

    devel oped

    usi ng

    t wo

    d i f f e r e n t appr oaches

    .

    Appr oach

    I

    d ea l s w t h

    t h e

    case

    wher e

    a va i l a bl e

    l and

    i s

    l i mted

    i n

    area

    or a

    basi n

    i s

    t o

    be

    s i z e d

    w t h a gi ven

    t o p

    surf ace

    area and a peak operati ng head t o be deter m ned

      Appr oach

    I I d ea l s w t h t h e case

    wher e

    abasi n

    i s

    t o be desi gned a t a gi ven peak operati ng

    head .

    The r e s p ec t i v e

    desi gn procedures

    f o r

    Appr oaches

    I and I I

    a r e i l l u s t r a t e d by exampl e probl ems i n Appendi x

    2 . 7   1

    Compute ProgramRECH RGE

    The

    FortnumprogramRECHARGE, NA~i i ch c o n s i s t s

    of

    a mai nprogram

    and

    four

    subr out i nes

    ( SI E`TE,

    FLOW H TAand TAHI ) ,

    was

    devel oped e s pe ci a l l y f o r basi n

    desi gn . Thi s program i s desi gned t o run on an I BM

    PC-AT,

    P- XT, PS/ 2

    m cr ocomput er o r

    any I BMcompat i bl e .

    The

    n f i l t r a t i o n

    equat i on

    was

    i ncorpor ated

    i n t o

    the

    program

    t o r e p r e s e n t

    unsaturated,

    u n s t e a d y - s t a t e

    f l ow t hr ough s o i l s

    .

    The f o r m

    of

    nput i s i n t e r a c t i v e .

    Theprogram

    i s

    wr i t t e n

    t o enabl e

    t h e

    desi gner t o makemul t i pl e runs of

    t h e

    basi n

    a n a l y s i s

    f o r gi ven

    s o i l pr o p er t i e s and i n f l ow

    q ua nt i t i e s

    . The

    sequence

    of programo pe r a t i o n , i nput

    data

    EB07-039 Page 20 of 28

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    and out put sequences and e r r o r mes sages a r e l i s t e d i n Appendi x B  A l i exampl e

    of

    comput er

    i nput and

    output sununar y s

    shoNN7n

    i n Appendi x C  i s t i n g of program

    RECH RGE s i ncl uded i n

    appendi x

    The NewYork S t a t e

    Depar t ment of Transport at i on wi l l not be responsi bl e f o r

    any

    r e s u l t s obt ai ned f r o mt h e use

    of

    shared comput er pr ogr ams or s t o r e d data . i ncl udi ng

    d i r e c t

    i n d i r e c t

    o r

    s pe c i a l

    or consequent i al damages . No e c hn i c a l support wi l l be

    provi ded

    .

    No

    warr ant i es

    a r e ext ended or

    g r a n t e d . ei t h er

    expressed or i mpl i e d wi t h

    r e s p e c t

    t o t h e

    accuracy

    and/ or

    per f or mance

    of

    any

    mat eri al s

    provi ded

    .

    The

    mat e r i a l s

    provi ded may

    be

    reproduced

    by

    t h e

    recei vi ng

    agency but may n o t

    be

    gi ven

    t o

    anot her

    agency

    wi t hout t h e perm ssi on of t h e NYSDOT 

    EB07 039 Page of

    8

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    3

     

    CONSTRUCTION

    GUDELINES

    3

    . 1

    Const r uct i on

    As basi n excavat i on

    i s

    a source of 1 1 1 1 f o r e n i b a i i k n i e n t s , excavat i on

    i s

    usual l y desi red

    e a r l y

    i n

    pr o j ec t

    c on s t r uc t i o n

    .

    However ,

    t r a n s p o r t

    o f

    excessi ve

    qua nt i t i e s

    of

    t i n e

    sedi ment s

    i n t o

    the

    basi n

    f r o mst orms occur r i ng dur i ng t h e

    pr o j ec t c o n s i r l i c t i o n

    peri od wi l l reduce or i mpai r t h e

    expect ed

    per f or mance

    of

    t h e basi n

      I f

    p r o t e c t i o n

    of

    t h e

    basi n under

    const r ucti on

    i s not

    provi ded and

    damage

    o c c u r s ,

    t hen c o r r e c t i v e

    ( r e s t o r a t i v e ) mai nt enance

    wi l l

    be t h e

    r equi r ed r ecour se

     

    r econm ended

    way

    of

    avoi di ng

    t h i s pr obl em at no

    addi t i o na l

    c o s t i s t o

    sequence

    t h e

    s t e p s

    i n

    const r ucti ng

    t h e bas i l w t h t h e

    work on

    he ni a f l p r o j e c t   Thus

    i s descr i bed bel owa s

    a

    t t v o - s t a g e

    operat i on

     

    The

    basi n

    i s i n i t i a l l y

    excavat ed e a r l y

    i n

    c ons t r uc t i o n, l eavi ng

    a I f t

      ( 0

    . 3 m t hi ckness of mater i al

    over t h e

    f i n a l

    f l o o r e l e v at i o n  

    Dr ai nage

    f r o mt h e p r o j e c t wat er shed duri ng

    const r ucti on

    may

    t hen

    be l e d

    t o t h e

    basi n

    i f necessary

     

    I f heavy

    i nf l ow

    occurs, br i ngi ng excessi ve

    sedi ment ati on of

    f i n e s ,

    t h e sur f ace

    wi l l

    mud- cr ack

    a f t e r

    dry i ng  

    At t h i s

    t i me t h e surface shoul d be

    ski mmed

    o f f p r i o r

    t o subsequent st or ms  

    When he pr o j ec t

    i s

    n ea r l y compl et e and per manent er osi on c on t r o l s a r e i n pl ace t hroughout t h e

    basi n

    wat er shed

    ; excavate t he basi n t o f i n a l l i n e s

    and

    g r a d e , r emovi ng t h e e x c e s s

    na t u r a l

    s o i l

    and

    sedi ment  

    Care

    shoul d be e xe r c i s e d dur i ng

    t h i s s t e p

    t o avoi d

    excessi ve

    compact i on of t h e basi n

    s u r f a c e s  

    Then

    seed or sod a s descr i bed i n

    Sec

      3

    . 4 ,

    c o ns t r u ct t he per manent i i n l e t s )

    and connect

    t o t h e s t o r mdrai n system 

    3 . 2 Wat er shed Er osi on Cont r ol

    Cl ose a t t e n t i o n

    t o sound erosi on

    c ont r o l

    pr a c t i c es 6

    g

    i n

    t h e wat er shed

    wi l l r e s u l t

    t o l e r a b l e

    sedi ment

    deposi t i on i n

    t h e basi n and keep mai nt enance c o s t s

    t o a i ni ni t mum The quant i t y

    of

    s i l t

    cont ai ned i n wat er

    f l ow ng

    i n t o t h e basi n

    by

    er osi on wi l l vary

    i

      oni s t o r n i t o s t o r m

    dependi ng on

    many a c t o r s ,

    but

    a s an

    annual aver age ;

    concent r ati ons o f s o l i d s up t o

    about 1, 000 ppmcan

    pr obabl y be a s s i m l a t e d

    by

    a

    basi n f l o o r w t h a vi gorous stand of

    t u r f ( s e e

    Sec   3 . 4 )   Thi s

    i s

    equi val ent t o about

    1

    ton of

    s o l i d s

    f o r each

    32, 000 f t

      of wat er

    ( 1 kg

    of

    s o l i d s

    p e r l l i of wat er )

     

    I f

    t h e ea r t h s l o pe s

    i n

    t h e wat er shed a r e provi ded w t h t h i c k

    vegetat i ve

    c o v e r , and di t c h es

    o r

    channel s a r e s ui t a b l y

    protected f r o m

    e r o s i o n , s o l i d

    concent r ati ons of

    one- hal f or l e s s of

    t h i s

    f i g u r e

    a r e r easonabl e

    expectat i ons

     

    Good

    er osi on c o n t r o l

    i n

    t h e wat er shed can pr oduce

    p r a c t i c a l l y mai ntenance- f r ee r echar ge s i t e s

    w t h

    t u r f

    l o o r s   Ont h e other hand,

    poor

    a t t e n t i o n t o

    er osi on c o n t r o l i n t h e wat er shed can r e s u l t i n

    excessi ve

    mai nt enance, cause

    poor

    publ i c r e l a t i o n s

    and envi r oi unent al or he al t h pr obl ems  

    I n

    ur ban

    a r e a s ,

    a

    por t i on

    of t he

    wat er shed

    area o f t e n

    may

    i e

    out si de

    of

    S t a t e

    r i ght - of- way

     

    I f

    const r ucti on a c t i v i t i e s

    occur i n t h e s e a r e a s , those r esponsi bl e f o r desi gn shoul d e s t a bl i s h

    t empor ar y and

    per manent er osi on c o nt r o l s as r equi r ed t o

    p r o t e c t

    t h e recharge area f r o m

    excessi ve

    s i l t a t i o n

     

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    3 . 3 I n l e t Desi gn

    Thef undament al consi der at i on f o r basi n i n l e t desi gn

    i s

    t h e prevent i on of scour a t t h e

    c u l v e r t and

    a t t h e basi n f l o o r   Thi s t h e

    peak

    ent r ance v el o c i t y

    of

    nf l ow t o t h e basi n

    must

    be

    hel d

    wi t hi n

    l i m t s by s u i t a b l e desi gn of t h e upstr eamstonn dr ai n

    systemand

    t h e i n l e t i t s el f   Ref er t o

    Ref

      6

    s p e c i f i c a l l y Sect i on 3 . 5 . 2

    and

    3 . 5 . 3 ) f o r p r o t e c t i v e aprons, ener gy d i s s i p a t o r s

    and

    s t i l l i n g basi ns

    NNhen

    s t e e p

    g r a di e n t s

    and

    hi gh v e l o c i t i e s cannot be

    avoi ded

     

    Runof f

    f r o msur r oundi ng

    l and   f l owi ng t owar d

    t h e

    basi n   shoul d be

    i n t e r c e p t e d by o p- o f - s l o pe

    g u t t e r s and

    c o l l e c t e d f o r gui ded di schar ge i n t o t h e mai n basi n i n l e t s  

    3

    . 4 Tur f

    Es t a bl

    shni ent

    Sur f aces of t h e s i d e s l o pe s

    and f l o o r

    shoul d be seeded, a s t hey r e p r e s e n t t h e

    f l ow

    area of he

    basi n  

    Dense tur f

    not onl y

    prevents

    er osi on and sl oughi ng

    of

    he s l o p e s , b u t

    a l s o provi des a

    nat ur al

    means of

    mai nt ai ni ng r e l a t i v e l y hi gh i n f i l t r a t i o n

    r a t e s

     

    Devel opment

    of thi ck vi gor ous

    t u r f

    i n

    t h e

    basi n

    i s

    a s e l f - ma i n nt a i l un g f e a t u r e

    f o r

    a

    r echarge

    s i t e

    once

    er osi on

    c o n t r o l

    i s

    s a t i s f a c t o r i l y

    e s t a b l i s h e d

    i n

    t h e

    wat er ; - s h e d See Sect i on 3 . 2 )

    .

    3 . 4

    . 1

    Topsoi l

    Topsoi l n a t i v e t o t h e s i t e and stockpi l ed p r i o r t o excavat i on

    may

    be

    used

    t o a i d i n

    tur f establ i shment  

    Car e

    shoul d be t aken t o avoi d excessi ve compact i on of t he

    seedbed so

    t h a t

    t h e

    new

    o o t s

    have l i t t l e d i f f i c u l t y

    i n n t aki ng

    hol d  

    3 . 4 . 2 F e r t i l i z a t i o n

    compl ete

    s t a r t e r f e r t i l i z e r

    such

    a s 10- 6-4

    i s

    r ec ommended t o

    encour age deep

    r o o t

    devel opment

    .

    Appl y a t a r a t e of 1, 000 l b s per

    a c r e ,

    a pp r ox i i n na t e l y 23 l b s p e r 1, 000

    t 1 ` 1 kg

    per 10m

      when

    prepar i ng

    t h e

    seedbed  

    These

    general

    c r i t e r i a

    shoul d be

    r evi ewed

    wi t h

    t h e

    Regi onal Landscape

    Ar c h i t e c t

    t o ve r i f y

    t h e i r

    a p p l i c a b i l i t y

    t o a

    s p e c i f i c

    s i t e

     

    3

    . 4 . 3

    Seedi ng

    The b r i e f per i ods

    of

    nundati on

    i n

    a r echarge area a r e

    no

    pr obl em

    f o r most

    gr ass

    s p ec i e s   Dr ought - r esi st ance,

    however ,

    i s an

    i mpor t ant

    consi der at i on

     

    The

    Regi onal

    Landscape A r c I i i t e c t

    shoul d

    be consul t ed

    r egar di ng

    an

    appr opr i at e seed f o r

    a

    gi ven

    cl i mat e and s o i l

    c o n d i t i o t l

    The pl acement

    of

    sod i nay be

    advi sabl e i n

    t h e

    v i c i n i t y

    of t he i n l e t and p r o t e c t i v e

    apron  

    The

    sod

    wi l l

    n o t onl y b e t t e r r e s i s t er osi on ar ound t h e i n l e t dur i ng a s to rm

    before

    t h e g r a s s

    g e t s

    a

    f o ot ho l d ,

    but

    wi l l al so hel p

    sl ow

    down

    v e l o c i t i e s as

    t h e

    i nf l ow

    spr eads

    over t h e

    f l o o r

     

    Mul ch

    shoul d

    al ways

    be

    empl oyed

    over t h e

    newl y

    seeded

    s u r f a c e s f o r p r o t e c t i o n , moi st ur e r e t e n t i o i i and e a r l y ger m nat i on of he seed

     

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    M NTEN NCEGUDELINES

    4 . 1

    General

    Thepr i mar y r equi r ement f o r assur i ng t h a t a recharge basi n cont i nues t o

    perform

    as untended i s

    peri odi c

    mai nt enance

    a s di c t a t e d

    by

    t h e

    r e s u l t s

    of

    r e gu l a r l y schedul ed i ns pe c t i o ns

    and

    eval uati ons . Not i ng war ni ng

    sympt oms

    e a r l y ,

    i n s t e a d

    of wai t i ng f o r a maj or

    per f or mance

    pr obl emt o o c c u r ,

    o f t e n c r e a t e s

    a s i t u a t i o n wher e a q u i c k , si mpl e

    and

    i nexpensi ve cure i s

    possi bl e

      F or t u na t e l y , t h er e may

    be

    a l a g of years

    bet ween t h e

    i r s t appear ance

    of

    s ympt oms and

    a

    sudden

    trend t o

    non- per f or mance

      Thi s chapter expl ai ns

    howper f or mance

    pr obl ems

    devel op

    w t h recharge b a s i n s , then

    c l o s es

    w t h a t a b l e

    s u r l u n >s  

    i z i ng t h e

    readi l y obser vabl e sympt oms,

    e f f e c t s and t h e

    cor r espondi ng c o r r e c t i v e r ecommendat i ons

    .

    4 . 2 Basi n Per f or mance Decl i ne

    The

    r n a j o r cause

    of

    di mni shi ng basi n

    per f or mance

    i s cl oggi ng

    of

    t h e i n f i l t r a t i o n surface  

    Thi s

    occurs

    by

    a successi on

    of

    e v e n t s   F i r s t ,

    f i n e

    sedi ment s i n t h e i nf l ow s e t t l e out and accumul at e

    over t h e

    i n f i l t r a t i o n

    surface over a peri od

    of

    t i me   Second,

    i n f i l t r a t i o n

    does not occur as rapi dl y

    as bef ore and

    soon

    t h e r e i s a

    sust ai ned

    per i od of

    t i me

    ` , h er e t h e basi n does not dry out f o r sever al

    weeks because

    of

    t h e accumul at ed

    s i l t

    coupl ed w t h f r equent

    r a i n f a l l

    .

    I t

    i s dur i ng

    t h i s

    pe r i o d,

    when

    favored

    by

    hi gh

    t emperatures , t h a t

    t h e t h i r d event t akes pl ace - - s t r a i n s of mcrobi ol ogi cal

    growt hs

    r api dl y pr opagate, cl oggi ng t h e l a ye r of i ne

    sedi ment and

    i n t e r f a c i n g s o i l pores s t i l l

    f u r t h e r w t h what i s b e s t

    descr i bed

    as sl i me I f t h e basi n

    does

    dry

    o u t ,

    these

    col oni es

    d i e and

    t h e surf ace uncl ogs . I f t does not dry o u t , the col oni es cont i nue grow ng,

    r educi ng

    t h e

    p r o b a b i l i t y of ever dr yi ng o u t   Thi s s i t u a t i o n l eads t o a t r ansf ormati on

    wherei n

    t h e

    b as i n

    bec omes a mor e or

    l e s s

    per manent

    body

    of

    st andi ng wa t e r ,

    NAFi th

    onl y

    i t s

    upper

    s i d e

    s l o pe s s t i l l

    abl e t o i n f i l t r a t e s to rmwat er i n

    any

    appr eci abl e quant i t y  

    Theabove scenari o

    i s not

    i nev i t a bl e

    and can

    be

    avoi ded

    e n t i r e l y

    .

    The

    key i s

    t o pr omot e

    dryi ng

    o u t f ol l ow ng a s torm 

    Ver y modes t

    contr ol

    of wat er shed

    er osi on (Sec   3 . 2 )

    coupl ed w t h

    vi gorous

    t u r f i n

    t h e basi n

    as

    next

    di s c us s ed,

    can ne ut r a l i z e t h e sedi ment at i on pr obl em

    whi ch

    otherw se

    s t a r t s t h e per f or mance d ec l i ne c yc l e  

    Dr yi ng o u t ,

    however ; i s s t i l l

    e ss ent i a l

    and t h e

    g r a s s

    wi l l hel p

    achi eve

    t h i s condi t i on. Keepi ng

    t h e basi n shal l owf o r good

    a i r

    c i r c u l a t i o n

    a s s i s t s

    t h e g r a s s

    t o

    compl et e

    t h e

    j ob r e s ul t i ng

    i n

    a basi n

    whi ch

    can be p r a c t i c a l l y

    mai ntenance- f r ee

     

    4 . 3

    Tur f as

    a Prevent i ve of Decl i ne

    Tur f on

    t h e basi n f l o o r and

    s i d e

    s l o pe s has f i v e b e n e f i c i a l

    f i i n c t i o n s

    as f ol l ows :

    1   I nc r e a s es s o i l p o r o s i t y and

    i n a i n t a i n s ,

    s t a b l e granul at i on and t h e r e f o r e , hi gh

    i n f i l t r a t i o n

    capaci t y

    due

    t o root

    gr owt h  

    2   I nc r e a s es t r a n s p i r a t i o n

    of

    wat er l eadi ng

    t o

    subsequent dryi ng out of s o i l  

    3

     

    Pr omot es

    de s i r a bl e

    b i o t i c

    a c t i v i t y

    l eadi ng

    t o

    g r e a t e r

    a i r

    and

    wat er

    permeabi l i t y

     

    4   When i n f l o w t o t h e basi n i s r a p i d , r e s i s t s t h e c u t t i ng a c t i o n

    of

    wat er c u r r e n t s and p r o t e c t s

    a ga i n s t erosi on i n t h e basi n

    i t s e l f

    Pr ovi des t h e a b i l i t y t o as s i m l a t e l i g h t

    sedi ment

    deposi t i ons

    and

    rapi dl y convert them

    i n t o t h e

    gr owt h

    support i ng l a ye r .

    EB07 039 Page 2  of 28

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    I n

    t h e

    absence

    of

    heal t hy vi gor ous

    v eg et a t i o n, t he s e

    f i v e b enef i t s

    a r e

    l o s t and t h e i r

    o pp os i t e s

    appl y  

    4 . 4

    hspect i on and Troubl eshoot i ng

    The p r i n c i p l e f i i n c t i o n of per i odi c i nspecti on

    i s

    t o d e t e c t

    and

    c o r r e c t

    any

    source of heavy

    sedi ment

    deposi t i on f - o mt h e

    wat er shed and any

    adverse e f f e c t s f r om i t over

    t h e

    recharge area  

    Tabl e 2 pr ovi des a gui de

    f o r

    condi t i ons

    t o

    l oon

    f o r ,

    t h e i r

    e f f e c t

    upon per f ormance

    i f

    not

    at t ended

    t o ,

    and

    t h e

    c o r r e c t i v e

    a ct i o n

    t o be t aken  

    Rul es

    a r e o f t e n desi r ed t o s e t

    a f i xed

    i nt e r v al f or maki ng b as i n i n s pe c t i o ns   Unf or t unat el y,

    a

    d es i r a b l e i nspect i on

    f r equency

    v ar i e s w t h i ndi vi dual

    wat er shed

    condi t i ons

    and

    r e c e n t storm

    a c t i v i t y   An

    adequat e f r equency

    f o r

    one basi n

    i n a gi ve

    t i me per i od

    may

    be i nadequat e

    ( o r

    excessi ve) f o r ot her

    b as i n s

    i n

    t h e same

    t i me peri od  

    However , somer u l es

    a r e under st andabl y

    d es i r a b l e

    and

    t h e

    fol l ow ng a r e

    suggest ed

    :

    I nspect

    a l l

    basi ns

    fol l ow ng

    anv

    major s t o r n 1

    causi ng

    l o c a l f l oodi ng or

    hacked up

    storm

    sewer s i n

    t h e

    l o c a l

    area ( Town,

    Count y)

     

    I nspect

    t i n y

    basi ns

    wher e ma _ j or c o n s t i - t l c t i o n a c t i v i t y

    i s

    t aki ng pl ace i n

    t h e i r wat er shed

    a r e a s fol l ow ng

    any storm

     

    Al so hi spect erosi on

    pr ot ect i on adequacy at t h e const r uct i on s i t e s

    at

    t h e

    same t i mes  

    4 . 5 Removal of

    Accumul at ed

    Sedi ment

    As out l i ned i n t h e

    Envi r onment al Procedures

    Manual ,

    Chapt er

    5

    . 1

    Hazar dous Wast e

    and

    Cont am nat ed Mat e r i a l ,

    pr o j ec t manager s,

    desi gner s

    and Regi onal Envi r onment al Uni t s shoul d

    s c r e e n

    a l l pr o j e ct s

    f o r

    hazar dous

    wast es and cont am nat ed

    ma t e r i a l s

    i f t hey i nvol ve excavat i on or

    o t h e r

    di st ur bance

    of

    t h e

    s o i l

     

    Thi s

    i s

    i ntended

    t o

    hel p

    a s s e s s

    the

    natur e

    and

    e x t e n t

    of

    cont am nati on and under st and how o pr oper l y

    manage

    or cl eanup vari ous hi nds

    of

    contam nant s t o compl y N A T i t h

    f e de r al

    and

    S t a t e

    r equi r ement s  

    P r i o r

    t o r emoval

    of

    accumul at ed sedi ment .

    Depar t ment s t ag

    shoul d performa cont am nat ed

    mat er i al s  

    s c r e en i n gs ,

    or a

    Phase

    I

    a s s e s s m e n t

    as descr i bed i n Ch  5

    . 1

    t o det erm ne

    whet her

    ad di t i onal

    st udy or t e s t i n g i s necessary

     

    I f the r e s ul t s of an assessment i nd i c a t e cont am nati on, Sect i on

    205

    of t h e

    Standard

    S pe ci f i c at i on s

    d es c r i b es

    how

    o t e s t

    and di spose

    of

    cont am nat ed

    s o i l  

    E 07 039 Page 5 of 8

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      Subsequent

    t o

    approval f r o mN SDEC

    or

    o t h e r

    l o c a l

    water a ut h or i t i es

    e s pe ci a l l y

    on Long I s l a n d ) , permssi bl e dosage r anges a r e

    as

    fo l l ows :

    E 07-039 Page

    6

    of

    8

    Tabl e L i spect i on

    and

    Troubl eshooti ng

    Gui de

    Condi t i on Noted Effect UponPerformance

    Corr ect i ve Acti ons t o

    be

    Taken

    Fl oor erosi on and scour hol e near i n l e t Advers e

    t o t u r f

    mai nt enance and s a t i s f a c t o r y 1 Lower v e l o c i t y of ent eri ng

    wat er by

    usi ng

    l ong tern per f or mance Mayunder m ne ener gy

    d i s s i p a t e r s ,

    s t i l l i n g p oo l , or both

    apr on

    or

    c u l v e r t Unsi ght l y . 2 . Refer

    t o

    Ref

    9 f o r

    protecti on

    desi gn

    Appearance of sedi ment over t oppi ng

    t u r f Adver se t o t u r f mai nt enance

    and

    s a t i s f a c t o r y

    1 I mmedi at el y l o c at e and c o r r e c t source of

    l ong tern perf or mance sedi ment

    i n t h e

    wat er shed

    2 When

    l o o r

    i s

    d r y , r emove

    patches

    of

    sedi ment wher e

    t u r f

    has been covered, and

    r e - e s t ab l i s h turf

    Constr i cti on a c t i v i t y

    i n

    wat er shed

    May

    l oad basi n w t h sedi ment

    i f

    adequat e l Requi r e

    t empor ar y

    di versi on of storm

    precaut i ons

    a r e n o t

    taken runoff

    f r o m

    r eachi ng

    recharge

    a r e a , o r

    2

    See

    t h a t proper

    t empor ar y and per manent

    erosi on c o n t r o l s a r e i n s t i t u t ed

    Weeds

    As s i s t t o

    mai ntai n i n f i l t r a t i o n

    r a t e s ,

    b u t

    may

    1 . Regul ar mow ngof turf

    provi des

    good

    be

    u ns i g h t l y , cr owd o u t t u r f ,

    and become

    a

    weed c o n t r o l Herbi ci des maybe

    used

    f i r e

    hazar d accor di ng

    t o i n s t r uc t i o ns i n

    s i m l a r

    f ashi on t o t h e adj acent

    wat er shed

    Lack of nor mal dr yi ng o u t

    a f t e r

    a storm Canqui ckl y

    becomeextr emel y

    adverse t o l Tr eat st andi ng wat er

    t o

    k i l l o f f t h e

    perf or mance Caused by

    negl ect

    of r egul ar mcrobi al g r o N v t l l s , usi ng

    c hl o r i n e or

    preventat i ve

    i nspecti on

    and t i mel y copper s u l f a t e

    i n

    r ecor mni ended dosages

    corr ecti on

    of

    mnor probl em

    Provi des 2 When

    d r y ,

    r emove

    accumul at ed

    sedi ment

    envi r onment f avorabl e

    t o

    s o i l - c l o g g i n g and c o r r e c t cause of excessi ve

    mcrobi al g r oNA~t l r s such

    a s a l g a e,

    s l i me s ,

    and sedi ment ati on

    i n wat er shed  

    f ungi 3 Re - e s t a b l i s h

    t u

    r f over t h e basi n f l o

    or

    N i nimmn Effecti ve Maxi mmn Perm ssi bl e

    Copper

    Sul f ate

    0 . 0 1 pprn ( 0 . 8 l b = 1 0 6

    g a l ,

    0 . 1 k g / 10

    -

    L) 2

    . 0 ppm

    ( 16 . 211: ' 10 g a l ,

    2 . 0

    k - /

    106

    L)

    Chol ri ne

    1

    . 0 ppm

      8

    . 3 1 b r / 1 0 6

    g a l ,

    1

    . 0

    kg/ 106

    L) 2

    . 0

    ppm

    ( 16

    . 6 l b l l

     

    ) 6

    g a l ,

    2

    . 0

    kg/

    1 0 6

    L)

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    REFERENCES

    Weaver R  J   Recharge Basi ns fo r Di sposal of Hi OmNvay StormDrai nage, Research

    Repor t

    69- 2,

    Engi neer i ng

    Research andDevel opment Bureau

     

    New

    York

    State Depart ment of

    Transport at i on,

    May

    1971

     

    2  Weaver R 

    J

      andkut hy, R  Fi el d Eval uat i on of echar ge Basi n, Research Repor t 26,

    Engi neer i ng Research

    and

    Devel opment Bureau, NewYork State

    Department of

    Transport at i on,

    February 1975  

    3  Rai nf al l I i l t e i l s i t y - D u r a t i o n - F r e c t u e r n c y

    Curves

    for

    Sel ected Stat i ons

    i n

    t he

    Uni t ed

    Sates,

    Al aska, HaXA a i i a r n

    I sl ands

    . andPuerto

    Ri co, Techni cal Pater No   25,

    Weather

    Bureau, US

    Depart ment

    of Conmnerce, December

    1955,

    P  31  

    4

      Vi essman,

    J r

    .

    et  

    a

     

    I nt roduct i on

    t o Hydrol ogy,

    New

    York:

    Harper and

    Row

    2 d

    Edi ti on, 1977  

    Hyd1 O OoV

     

    Engi neer i ng

    Handbook Secti on

    4

    S o i l

    Conservati on

    Servi ce 

    US

    Department of

    Agri cul t ure, 1972

     

    6  Bankand Channel

    Protecti ve Li ni ng

    Desi gn Procedures

     

    Soi l Desi gn

    Procedure

    SDP-2 Soi l

    Mechani cs Bureau, New

    York

    State Department of Transportati oi L August 1971  

    7

     

    Const ruct i on Gui del i nes for TemporaryErosi on Cont rol s

    .

    Const ruct i on Subdi vi si on,

    New

    York

    State Depart ment of Transportat i on, Apri l

    1974

     

    8

      Temporary Soi l Erosi on

    and

    Water Pol l uti on Cont rol ,

    Secti on 209,

    St andar d

    Speci f i cati ons, NewYork State Department of

    Transportat i on,

    J anuar y

    1985

    PP  2- 25

    t hrough 2- 27

    .

    9

      Pet erka,

    A, J

      Hydrati f c

    Desi gn of

    S t i l l i n g Basi ns

    andEnergy

    D ssi pator

    : s Bureau of

    Recl amat i on_ US

    Department of t he

    I n t e r i o r

    J ul y 1963  

    EB07-039 Page 27 of 28

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    APPENDCES

    E 07 039 Page 8 o 8

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    APPENDXA

    EXAMPLE

    PROBLEMS MANUALCOMPUTATIONS)

    Rat i onal r echar ge basi n desi gn i s arr i ved a t t hrough a combi nat i on of hydr aul i c and s o i l s

    engi neeri ng

    f unc t i o ns   The mos t i mport ant el ement s af ect i ng basi n

    s i z e s a r e

    adequat e assess ment

    of

    l o c a l mas s i nf l ow and

    accur ate pr edi cti on

    of wat er

    i n f i l t r a t i o n

    i n t o t he under l yi ng s o i l s   Spe c i f i c

    i nfor mati on r equi r ed f o r desi gn c ons i s t s of t he desi gn stonn runoff

    dat a

    f o r t he l o ca l wat ershed,

    dept h

    t o

    gr oundwat er

    t a b l e

    and

    unsaturated

    pr o p er t i e s

    of

    t h e

    cohesi onl ess

    s o i l

    i n t o

    whi ch

    t h e

    wat er

    wi l l

    i n f i l t r a t e  

    The

    necessary s o i l pr o p e r t i e s a r e

    s p e c i f i c

    g r a v i t y , nat ur al moi st ure c o n t e n t , s p e c i f i c

    surface a r e a , gr ai n

    s i z e

    d i s t r i b u t i o n , nat ur al p o r o s i t y , hydr aul i c conducti v i t y

    of

    t r ansm ssi on

    zone

     

    c a p i l l a r y sucti on po t e nt i a l

    and

    hydr aul i c d i f l u s i v i t y

     

    These a r e

    covered

    i n d e t a i l i n

    Ref  

    1

     

    The desi gner

    can

    choose

    one

    of two desi gn approaches,

    each

    of whi ch i s i l l u s t r a t e d by

    a l l

    exampl e

    pr obl em

     

    Appr oach

    I d ea l s

    w t h t h e case wher e a basi n

    i s

    t o be desi gned f o r a gi ven surface a r e a , but

    w t h basi n peak operat i ng head unknown

     

    Appr oach I I permts t h e basi n s i z e

    and

    di nensi ons t o be

    desi gned f o r a gi ven peak bas i l operat i ng head

     

    The procedures f o r c a l c ul a t i ng t he di ne- dependent mas s i nf l ow qua nt i t i e s a r e n ot presented here

     

    The

    reader may

    r e f e r t o

    Exampl e

    Pr obl em

      of

    Ref

     

    f o r d e t a i l s

    of t he met hod used

    i n

    t h e f o l l ow ng

    desi gn exampl e

    o r

    use any other appr opr i ate procedure f o r

    obt ai ni ng

    mas s nfow 

    APPROACH  

    US

    Cust omar y Uni t s )

    G ven

    : A

    echarge

    bas i l i s pr oposed

    t o

    di spose

    of

    hi ghway

    s t o r n i

    r unof f :

    Coor di nat es of

    he mas s

    i nfl oNv curve f o r t h e

    proposed

    basi n s i t e a r e l i s t e d be l ow  

    The

    a v a i l a b l e

    l and

    f o r

    basi l use

    i s

    l i m t e d

    t o

    210, 000

    f l

    The

    subsurf ace

    s o i l

    i s

    sandy

    s i l t

    w t h

    t h e

    f o l l ow ng pr o p er t i e s

    :

    Natural p o r o s i t y , i j =0. 4 0

    Hdraul i c

    conducti vi t y

    of

    t r ansm ssi on zone, k

     

    =

    2. 1 6

    f t / h r

    f r o m

    Equat i ons

    ( 1 ) , ( 2 ) ,

    and

    ( 3 ) )

    EB07- 039 A - 1

    Tul le

    hOl l S

    Infl ow

    Q

    nl . I 11l ol l ft3

    Tim

    OI 1 S

    I nf l ow

    Qi

    I I LI I l O

    f t )

    1 0. 0 8 10

    6

    . 4 8

    2 0. 1 6

    1 1

    7 . 1 0

    3 0. 5 0 12 7 . 6 0

    4

    . 1 1 1 3 7 . 9 4

    1 . 8 2

    14

    8 . 1 6

    6 2. 8 0 1 5 8 . 2 7

    7 3 . 7 9 16 8 . 3 7

    8 4. 8 0

    17

    8 . 4 2

    9

    5

    . 7 4 18

    1

    8 . 4 2

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    APPENDXA

    Capi l l ary suc t i on

    p o t e n t i a l ,

    yn

    =

    0

    . 1 8 f l

    .

    ( f r o mFi g

     

    4)

    Hydr aul i c

    d i f i u s i v i t y , o c

    =9

    . 3 2

    f t

    : h r

    ( f r o mEquat i ons

    ( 1 ) , ( 2 ) , ( 3 )

    and

    ( 4 ) )

    Dept h

    f r o m

    gr ound surface t o gr ound

    wat er t a bl e

    : = 50 f t  

    F i nd

    : Si ze

    and di mensi on

    of

    a squar e basi n pl an w t h

    1 v e r t i c a l o112 hori zont al s i d e s l o pe s  

    St ep l : - A c t u al

    mas s i l l t l o

    - \ V

    cu

    -

    \ es

    u

    c11 a s det er m ned f r o n t

    f i e l d

    i nst r ument at i on) usual l y

    wi l l

    have

    a t a i l o r i n f l e c t i o n a t

    e a r l y

    val ues of

    t i me

     

    The

    t abul ated

    dat a have

    t h i s

    c h a r a c t e r i s t i c , whi ch

    r e qu i r e s c or r e c t i o n

    t o t i me coor di nat es t o r emove

    t h i s

    t a i l   The

    met hod

    of

    e s t a b l i s h i n g t h i s

    t i me

    c o r r e c t i o n , 3 . 3

    h o u r s ,

    i s shown i n Fi gure 1A  The

    coor di nat es of t h e

    corrected

    mas s i n f l o w cure

    a r e t a bu l a t e d

    bel ow

     

    I f

    t h e

    mas s i nf l owcur ve

    i s

    cal cul ated

    f r o mt h e

    pr ocedur es

    i n

    Exampl e Pr obl em

    1 of

    Ref :

    1 ,

    no t a i l

    i s

    obt ai ned

    and

    n o t

    t i me

    cor rect i on

    i s

    necess ar y  

    St ep 2

    :

    The equat i on

    f o r i i n f l t r a t i o n

    over

    t h e

    basi n

    ar ea i s :

    Q= 2k   A

     

    ( H/ 2 +

    y t , ) ~

    t

    /

    c

    a

    wher e :

    H/ 2

    = t h e

    aver age basi n

    oper ati ng head f o r t h e

    p e a l - desi gn s t o r m

    o r

    hal f

    of

    t h e maxi mum

    basi n

    oper ati ng head  

    A

    t h e

    basi n hor i zont al c r o s s - s e c t i o n a l

    ar ea

    o r pl an

    f l ow

    ar ea at

    I I / 2

     

    S u b s t i t u t i n g

    val ues of s o i l par amet er s

    i n t o t h e

    above

    e qu at i o n,

    gi ves :

    Q=( 2 ) ( 2 . 1 6 ) ( H/ 2+0 . 1 8 )

    J

    ( t / 2 9 . 3 )

    Af)

    Q=0. 798 ( H 2 - + - 0 . 1 8 )

    t ( _ f )

    St ep 3 : Est i mat e

    t h e

    r ange of

    t h e peak

    basi n oper at i ng head, I I , t o

    be

    used

    i n desi gn i n

    accor dance

    w t h

    t he f ol l ow ng assumpti ons :

    EB07-039

    A-

    2

    Tune

    yours

    Cor r ect ed

    I nf l ow

    m l l i o n

    f t

    3

    Tune

    l our s

    Cor r ect ed

    I nf l ow

    m l l i o n

    f t

    3

    1 1

    . 0 0

    10

    8

    . 0 0

    2 2

    . 0 5

    11

    8

    . 1 9

    3 3

    . 0 0

    12 8 . 3 5

    4

    4

    . 0 8

    13 8 . 4 1

    5 5 . 0 2

    14 8

    . 4 2

    6

    5 . 8 5 15

    8

    . 4 2

    7 6 . 8 5

    16

    8

    . 4 2

    8 7

    . 2 2

    17 8

    . 4 2

    9 7

    . 6 8

    18 8

    . 4 2

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    APPENDXA

    l   Frome xp er i e nc e , t h e

    f i n a l

    desi gn

    val ue of Q

    wi l l

    be bracketed wi t hi n t h e

    range

    of 0 . 2 9

    Qi p

    and 0 . 7 6

    Qi p

    ;

    wher e Q

    i , i s t h e

    cumul at i ve f l ow at

    t h e t i me when he

    c o r r e c t e d

    mass- i nfl ow curve s t a r t s

    peaki ng.

    2   Al so

    f r o mexperi ence,

    t h e

    area

    of t h e

    water

    s u r f a c e ,

    A,

    wi l l l i e wi t hi n t h e range

    of

    . 0 5

    Af

    and . 2 5 Af  

    The c o r r e c t e d mass- i nfl ow curve a s

    shown

    i n Fi g   l A n di c a t e s

    i t

    s t a r t s peaki ng

    appr oxi mat el y

    at c oo r di na t e s , t =8 hours

    and

    Q

    E ,

    =7

    . 3x106 f t

    3

     

    Su bs t i t u t i ng t h es e

    t wo

    number s

    i n t o

    t h e i n f i l t r a t i o n equat i on e s t a b l i s h ed i n St ep

    2

    and usi ng t h e t wo

    above

    ment i oned basi n

    operat i ng

    range

    c r i t e r i a , y i e l d

    t h e f ol l owi ng equati ons

    :

    wi t h A,

    =

    210, 000 f l ` , H, , = 28 . 9 0

    f l .

    and

    Hni n=

    9

    . 0 2 f l  

    Step

    4

     

    Repl ot or

    t r a c e t h e c or r e c t e d

    mas s i s i f l ow curve on a

    news h e e t

    of gr aph paper ( F i g

      B

    t o permt conveni ent superposi t i on of mas s

    i n f i 1 t r a t i o n

    curves f o r var i ous as sumed peak

    operat i ng heads

     

    St ep 5 For a square basi n wi t h

    1

    on2 s i de

    s l opes ,

    A

     

    can be expressed i n t er ms

    of

    I I and A

    as

    f ol l ows

    :

    Af

    = A,

    -4H~

    4

    H'

    The

    i n f i l t r a t i o n equat i on then becomes

    :

    Q

    =

    0. 798 ( H `2+0

    . 18)

    o   t

    A

     

    -

    4 I I ti 1

    +4

    H)

    Assume four

    val ues of t h e peak basi n

    operat i ng

    head

    bet ween

    H,

    and

    H, f i and

    comput e t h e cumul at i ve i n f i l t r a t i o n f o r conveni ent val ues of t i me f r o mt h e

    i n f i l t r a t i o n

    equat i on f o r

    each

    val ue of assumed Hhr oughout t h e t i me peri od of

    i n t e r e s t

     

    P l o t these

    four

    accumul at ed i n f i l t r a t i o n vs   t i me curves on t h e graph prepared i n St ep 4  

    Fi gur e B

    shows

    t h e f i na l p l o t a s

    i t

    wi l l appear at t h e end of t h i s s t e p

    .

    EB

    07- 039 A- 3

    0 . 7 6

    x 7

    . 3x10' = 0 . 798

    Hmx

    i 2+0 . 1 8 )

    ~

    8 1 . 2 5 )

    0 . 2 9 x 7 . 3x10

    6

    =0

    . 798

    Hz

    ;  

    % 2 +0

    . 1 8 )

    t i

    8 ( A , / 1 . 0 5 )

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    APPENDX

    0

    3

    . 3

    1

    Time hours)

    TimeC

    rrecti on

    t o

    Actu~ Data

    Fi gure

    1A

    TuneCorrecti on for Mass I nf l owCuve

    wth

    Tai l

    EB07 039 A 4

    2

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    10

    0

    APPENDX

    10

    115

    20

    Ti me hours)

    OA H=24

    92

    OcH

    =16

    . 97

    .

    OB

    =

    20. 9 5 f t  

    f t

    H=13 . 00 f t .

    Fi gure 1B

    Compari son

    of I nf l ow Outf l owRates

    EB07- 039 A- 5

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    APPENDX

    A

    Step

    6: I n

    Fi gur es

    1B, scal e of f the

    peak

    d i f f e r e n t i a l , Q, between the mass i nf l ow

    curve

    andeach

    of the i n f i l t r a t i o n curves . Thi s

    i s

    most conveni entl y donewi t h di vi ders . Cal cul ated t he

    basi n

    vol umes

    for t he

    gi ven val ue

    of A, and for each

    val ue

    of

    assumed

    peak bas i l

    oper at i ng

    head

     

    The

    f o l l ow ng

    t abl e

    pr ovi des

    si mpl i f i ed

    f ormul ae

    for

    square,

    rectangul ar,

    and

    c ir cul ar basi n

    pl ans .

    where : P , , =peri meter of basi n

    bottom

    P,

    =

    per i meter of

    wat er

    sur f ace

    whenbasi n

    operat i ng

    head

    equal s

    H,

    =

    area of basi n

    bottom

    _

    =area of

    basi l

    top when

    basi n

    operat i ng headequal H,

    S= si de

    sl ope

    1 vert i cal

    :

    S

    hori zontal

    or cotangent of t he

    angl e

    bet ween

    t he

    basi n s i d e

    sl ope and

    a

    hori zont al

    pl ane

    .

    =3

    . 1416

    Next determne t he

    di f f erence

    between

    OQ

    and

    basi n

    vol ume, and

    t abul ate

    the

    i nf ormati on as f ol l ows :

    Step7  Graphi ca l l y p l o t

    AQ

    -

    Basi n Vol ume

    val ues agai nst Hand

    draw

    the

    curve

    as i n Fi gur e

    1C  Thepeak basi n

    oper at i ng

    headHequi r ed for t he

    basi n

    i s i ndi cat ed by t he poi nt of

    i ntersecti on of the

    curve

    wi t h t he

    hori zontal

    a l i s , i n t h i s case,

    20R

     

    EB07- 039 A- 6

    f t . )

    : , Q

    10  f t )

    Bashi Volwi e

    ( 106

    f t

    AQ- Bashi Volwi e

    ( 106

    f t )

    13. 00 4. 90 2. 43 2. 47

    16. 97 4. 05 3. 06 0. 99

    20. 95

    3

    .25 3

    . 64

    - 0. 39

    24

    . 92 2

    . 65

    4

    . 18 - 1

    . 53

    Basi n

    Type

    P , , : 8 , - A

    b

    Basi n

    Vol ui ne

    Square

    and

    Rect angul ar

    P

     

    - 8SH

    SHP 

    +

    4SI )

    ( A ~ , +

     

    +  \ i A

    , A , - )

    H 3

    Ci rcul ar

    P, - 2HSz

    SHP

    b +r ESH)

    2

    :

     

    ) t ,

    A SHN ~x . A t , H/3

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    9z c r

    3

    2

    1

    - 20

    PPENDX

    Fi gur e CDeter m nat i on of Requi r ed

    Peak

    Operat i ng Head H

    EB07- 039 A- 7

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    Step

    8

    : Check  t

    o v er i f y t hat

    t h e d i s t a nc e

    f r o mt h e basi n

    f l o o r

    t o

    t h e

    groundwat er t a l b l e i s greater

    t han

    0. 25H f t

    .

    5 f t . ) s o t h at

    t h e

    devel oped

    i n f i n i t e

    depth i n f i l t r a t i o n t heory hol ds f o r

    t h e

    e n t i r e t i me

    span .

    I n t h i s

    c a s e ,

    t h e

    d i s t a nc e

    f r o m

    t h e

    basi n

    f l o o r

    t o

    t h e

    groundwat er

    t a b l e

    i s

    30

    f t

    .

    ;

    t h e r e f o r e

    t he t heory hol ds

    .

    Step 9 :

    I f t h e d i s t a nc e f r o mt h e basi n

    f l o o r

    t o t h e groundwat er was f ound t o be l e s s t han . 25H

    f t

    . , t he desi gn

    vol ume woul d have

    t o

    be

    obt ai ned

    t hr ough

    a

    combi nat i on of

    s t e ep er s i de

    s l o pe s

    or l a r g e r basi n surface area t han o r i g i n a l l y

    proposed .

    Det erm ne

    t h e r equi r ed

    basi n vol ume and

    area

    of basi n bottomusi ng

    t h e

    r e l a t i o ns hi p

    present ed i n Step 6 .

    D e s i a , j i Smunary  

    Top

    :

    Bottom

     

    Vol ume  

    Dept h :

    PPRO CH   I (US Customary Uni t s )

    Step 1

    :

    Step 2

    :

    Step 3 :

    Step

    4

     

    Wth

    t h e

    gi ven val ues of H

    f ol l ows

    :

    Q=81 2 _ \ /

    r

    tA

     

    PPENDX

    The

    basi n s i z e

    and di unensi ous

    are as

    f o l l ows

     

    458

    . 2 5

    f t . x

    458. 2 5 f l . ,

    Area =

    210, 000

    f t `

    378

    . 2 6

    f t

    . x 378. 2 6

    f t

    . ,

    Area

    =

    143, 000 f t

    2

    3, 509, 000 f t

    20 f t

    For

    t h e

    s ame subsurf ace condi t i ons and dat a

    gi ve

    i n

    t h e

    approach

    I exampl e probl em deter m ne

    t h e

    s i z e and di mensi ons of

    t h e

    basi n i f

    t h e

    proposed peal -

    basi n operat i nghead

    i s

    20 f t

    .

    The s ame as Step

    1

    i n

    t h e

    Appr oach

    I

    exampl e probl em 

    ,

    k

    t , and

    t h e

    i n f i l t r a t i o n

    equat i on i s

    e s t a b l i s h ed as

    Usi ng

    t h e s ame

    approach a s de t a i l e d i n

    Step

    3 of Appr oach I

    exampl e

    probl em

    est i mat e

    t h e range

    of

    t h e basi n surf ace area t o be

    used

    i n

    desi gn

    .

    Thi s

    l e ad s

    t o

    t h e f o l l ow ng two

    l i m t i n g

    i n f i l t r a t i o n equat i ons

    :

    0

    . 76

    x 7. 3x10` = 8

    . 1 2 1 f r

    8