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    Civil Engineering Design

    YearPopulation in thousand

    1951 951961 1701971 2201981 2501991 2802001 350

    Per capita water supply rate = 115 lpcd.

    Design period:

    o Pumping machinery = 15yr.o Treatment unit = 20yr.o Conveyance pipe = 30yr.

    Parameter

    o BOD(mg/l) = 225o PH = 7.2o TSS(mg/l) =225o COD(mg/l)=330

    Ig = (0.78940.29410.13630.120.25) 51

    Ig= 0.248

    P15=P01(1+Ig) 5.1

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    =350K(1+0.248) 5.1

    =487.96K

    P20=P01(1+Ig) 2

    =350K(1+0.248) 2=545.12K

    P30=P01(1+Ig) 3

    =350K(1+0.248) 3

    =680.31K

    Q15 (avg)=4900001150.810^-3=45080m 3 /day

    Q20 (avg)=541001150.810^-3=50149.2 m 3 /day

    Q30 (avg)=6803001150.810^-3=62587 m 3 /day

    Consider for monsoon

    Q15 (avg)=450801.1 = 49588 m 3 /day=0.573 m 3 /sec

    Q20 (avg)=50149.21.1=55164.12 m 3 /day

    =0.63 m3

    /secQ30 (avg)=62587.61.1=68846.36 m 3 /day

    =0.79 m 3 /sec

    Q15 (peak)=(Q 15avg) (P.F)+O.1(sewage)

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    =45080(2.25)/(243600)+0.1(45080)/(243600)

    =1.22 m 3 /sec

    Q20 (peak)=(Q 20avg) (P.F)+O.1(sewage)=50149.2(2.25)/

    (243600)+0.1(50149.2)/(243600)=1.36 m 3 /sec

    Q30 (peak)=(Q 30avg) (P.F)+O.1(sewage)=62587(2.25)/

    (243600)+0.1(62587)/(243600)

    =1.69 m3

    /sec

    Detention Time =20min

    V=Qt=1.361200=1632m 3

    Assume liquid Depth inwet well as 6m.

    Area= 61632

    =272m 2

    Assume diameter of dry well

    A= 4 (d2 -7 2 )

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    d =20.05Design of rising mainV =0.8 to 2.5 m/sAssume V= 1 m/sQ30 (peak) =1.69 m 3 /secA= V

    Q = 169.1 =1.69m 3 /sec

    Assume of 4 n.o.s. of pipe. Diameter of Pipe (d) =4/4(d 2)=1.6

    d=0.73 mHead loss

    Now, Hf=10.7852.1

    C Q

    C Q

    89.4 D L

    Where, C=Chazzysconstant(135)

    L=15m

    =10.7852.1

    413569.1

    ( ) 89.473.015

    =0.017mH=Hf+Hs

    =0.017+15=15.017 mHp of Pumps,

    =n

    H QSw75

    15 Where, n=0.7.

    = 7.075017.1522.11000

    =348.96 HpProvide 4 pump of 90 Hp

    Provide 4 pump for stand by Provide 8 Pumps

    1.Design Of Screen Chamber

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    Assume Velocity of flow throughscreen=0.8m/sec.

    Q peak 30 =1.69 m 3 /secOpen area of screen = V

    Q = 8.069.1 =2.112m 2

    Rectangular Bars of 1 cm width are providedat 5cm clear distance.

    Total Area =2.112 56 =2.534m 2

    Provide 2 Screen with one as stand by,

    Assume screen bar are placed at 60 withhorizontal.

    Total Area=60sin

    534.2 =2.92 m 2

    Assume Width of screen chamber =2.5mHeight of screen chamber=1.17m

    Velocity of flow above screenV=0.8 6

    5 =0.67 m/sHead loss through screen

    =0.0729(V 2 -v 2 )=0.0729(0.8 2 -0.6 2 )

    =0.014 mHead loss when screen is half clog=0.0729(1.6 2 -0.67 2 )=0.15

    2.Design of grit chamber

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    Minimum size of grit particle to be removed is0.2mm with Specific gravity of 2.65

    Vs=( )

    18

    12 s sd g

    ;=

    ( ))1001.1(18

    165.2)102.0(81.96

    23

    ;

    =0.036 m/sec.

    Re=

    d V s ;

    =01.1

    )102.0(036.0 3

    =7.128>1.Transcent flow condition,Vs= (0.707(Ss-1) d 6.06.1 ) 714.0 Where, d=0.2

    310 =0.025 m/sec

    Vc= (8K (Ss-1) f gd ) 21 ; Where, K=0.04;

    =0.186 m/sec f =0.03;Keep Vh=0.15 m/sec.As Q peak 20 =1.36 m 3 /sec.

    Q avg 20 =0.58 m 3 /sec.Assume Q min20 =0.41 m 3 /sec.Cross sectional area of grit chamber

    A peak =h

    peak

    V

    Q

    chamber gritof No.

    Provide 4 Grit chamber.A peak = 15.04

    36.1 = 2.26 m

    2

    A Avg = 15.0458.0

    =0.967 m2

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    A min = 15.044.0

    =0.67 m2

    A parabola = 32

    W Z0

    Assume width W= 2 m.2.26= 3

    2 2 Z 0 ;Z 0 =1.695 m.

    Now, Z 0 =CW 2 ;1.695=C 2 2 ;

    C = 0.42Z 0 =0.4 W 2

    A parabola = 32 W Z 0 ;

    = 32 W 0.4 W 2

    A parabola =0.28 W 2 ,

    Flow Area Z 0 WPeak =1.36 2.26 1.695 2Avg. =0.58 0.967 0.948 1.53Min. =0.41 0.67 0.396 1.27

    sh V D

    V L =

    max D

    LV

    V

    s

    h =

    L=1.695 025.015.0

    =10.17;

    Efficiency =1-n

    s AV n L

    1

    +

    ;

    Where = measure of settling basin

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    Take = 81

    for good performance,n =75%;

    0.75=1-8

    ...025.0

    81

    + ROS L ;

    S.O.R. = 0.01653 m/sec.Q peak 20 =1.36m 3 /sec.

    Actual S.O.R. =

    217.10436.1 =0.020 m/sec.

    3.Design Of Partial Flume:

    Provide 4 Grit chamber so that maximumflow rate in each is 436.1 =0.34.

    Throat width h =0.305,C=0.69,

    n =1.52,St=0.62,

    Flow in partial flumeQ=Cha n

    0.4=0.69Ha 52.1Ha=0.71 m.

    Assume width of 2.5m,Vh=0.25 m/s.

    At peak flow depth of flow in each is,d= VhChamber Gritof Width

    Chamber GriteachinQ

    ;

    = 0.252.50.41

    ; =0.66+0.3;

    =0.99m Provide 1md = H +a

    0.656 = 0.7+ =-0.044 m

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    Q 441.0

    min = =0.1m 3 /sec.Q=C ha H

    0.1=0.69Ha 52.1

    Ha=0.28 m d += a H min

    =0.28-0.044=0.236 m

    Vh at minimum flow,

    Vh=min

    min

    dChamber Gritof WidthChamber GriteachinQ

    ;

    = 0.2362.50.1

    =1.69 m/s.Surface area of grit chamber;= S.O.R.

    Q ;= 0.016531.36 ;

    =82.27 m 2Gross area of each,

    = 482.27 ; =20.57.

    DIMENSION OF GRIT CHAMBER

    So, Width =2.5 mLength= 8.5 m

    4.Design of primary settling tank:

    Q design = Q avg = 0.580For primary settling tank S.O.R. = 35 to 50

    m 3 /m 2 /dAssume S.O.R. = 40 m 3 /m 2 /d.

    S.O.R. = AQ ;

    A = 4058.0 ; =1253.73 m 2

    Provide 2 clarifierEach A= 2

    73.1253 ; =626.86m 2 .

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    A= 24 d

    ;d=28.25 m 30 m.

    Assume side water depth (SWD) =3.5 mVolume of each =2194.0 m 3

    Detention time = QV =

    58.0

    0.2194 =3782.77 sec=21.050=2.1 hr.

    Weir load ratry (WLR) = DQ

    WLR= ( )25.2828640058.0

    ; ( As 2clarifiers)

    = 282.464 m 3 /m 2 /d

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    =0.27m 0.30 m

    Assume 0.1 m head loss +0.5 m freeboard.

    Total depth = 0.6 m

    Assume suspended solid concentrationin sewage = 225 mg/lit.

    Further assume that 70% of removal of excess occurs in primary clarifier and outof total suspended solids 70% are volatile and 30% arein organic

    Or fixed.Q avg 20 =0.58

    Mass of sludge settled in eachprimmaryclarifier=2257.0

    258.0

    =45.67gm/sec.

    =164.43kg/hr.

    Assume specific gravity of inorganic solids =1.05Specific gravity of inorganic solids = 2.5.

    Overall Specific gravity of suspended solids=

    +=

    05.17.0

    5.23.01

    ST S

    ST S =1.27.

    += 27.1 05.0195.01SC S ; SC S =1.01.

    Volume of primary sludge,

    s P M

    V SLw

    SC

    .=

    ;

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    05.001.1100043.164

    = ;=3.25 m 3 /hr.

    Let the sludge be removed after every 4 hr,

    Volume of sludgestorage=(3.254)=13.02 m 3

    V= ( )( )

    ++ 21

    3r r

    hr ; Assume, h=1.5.

    13.02 = ( )( )

    ++ 21

    35.1

    r r r ;4.144= r+0.5 ( )( )21 + r r

    r = 2.74.

    Calculation of bottom slope clarifier,Bottom slope of D.C.= 8

    1to 12

    1 Assume 10

    1

    Accurate sludge unit:No. of aeration tank minimum 2. Side

    water depth i.e. liquid depth in (diffused)aeration tank =4.5 to 7.5 m. 1 to 6 m forsurface aeration . Usually 3 to 4.5. Freeboard . 0.3 to 0.6 m. For diffused aerationand 1 to 2.5 for surface aeration.Ratio of width to length of aeration tankB:L= 1:3 to1:4.

    B.O.D. 5 Of settle sewage =225 mg/lOutlet B.O.D. of treated sewage= 30 mg/l.Concentration of bio mass in treatedsewage =25 mg/lWith 65% bio-mass as degradable.

    SO=225 mg/lB.O.D. total =B.O.D. Sol +B.O.D. SS

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    Bio degradable bio mass in treatedeffluent= 0.6525

    =16.25 mg/lB.O.D. ult of bio mass= 1.4216.25,In treated effluent = 23.1 mg/l.

    703.0...... 5 =ult DO B

    DO B ; B.O.D. due to biomass=23.10.7

    =16.17 mg/l30=B.O.D. Sol 5 +16.17;B.O.D. Sol 5 =13.83 mg/l;

    Efficiency of treatment1. Based on Total B.O.D.= %95.801005.157

    305.157 =

    2. Based on Sol B.O.D.= %23.911005.157

    83.135.157 =

    Volume of aeration tank required:

    V=( )

    ( )cd esol cavg

    K

    S S Q

    +

    1

    0

    ;Where: = 0.5 mg/l c =10days

    d K =0.06 day 1

    Q d avg /544328640063.0 ==

    V=( )

    ( )( );

    1006.01300083.135.157105.054332

    +

    =8146 m 3Provide 2 aeration tank with 4m side water

    depth(SWD)S.A. of each A.T. = 42

    8146 =1018.3 m

    2

    B4B=1018.3 m 2

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    B =15.95m say 16mm L = 64 m

    Free board =1.0 mProvide 2 aeration tanks of 15.3m width and 64mlength & 5m total depth.

    =

    544324649.15

    2...

    T R H

    =0.149 day= 3.58 hr.

    Calculate sludge wasting rate;

    +

    = ew

    c QQVx

    Q ;

    Assume concentration of MLSS insludge recycle line as 10,000 mg/lit. Assumeconcentration of biomass in treated effluentas 80% of S.S.

    8.0=MLSS

    MLVSS ;X w =0.810000= 8000mg/l

    Q we QQ =X e =0.82520 mg/l.V=15.96442

    =8140.8 m 3

    +=

    eewwc QQ

    V Q

    ;

    ( )

    +=

    2054432800030008.8140

    10ww QQ

    ;

    Q w =169.62 m 3/d. =1696.2 kg /day

    Calculate O 2 required and Hp of surfaceaeration;

    B.O.D. 5 Removed= 157.5-13.83=143.67 mg/l

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    B.O.D. L = 27.21168.067.143 = mg/l

    Kg of B.O.D. removed;=54432211.27 1000

    1 ;

    =11500 Kg/dBio mass waste per day;=1696.20.8;=1356.96 Kg/d.Net O 2 required = (11500-1.42)

    1356.96=9573.1168 Kg/d=365.56 Kg/hr.

    Computation of power requirement for surfaceaeration,

    Mt= ( ) ;02.1 2010

    T

    s

    l sw

    C C BC

    R

    Mt= ( ) ;95.002.108.9224.81

    5.1 2025

    =1.08r P

    g

    H H Ok 2 ;

    Hp aeration required =08.1

    87.398 =369.33h p;

    Hp required in Aeration tank =66.186

    233.369 = h p

    So provide 8 aeration of 25 HpCalculate the re circulation ratio

    R= 3000)100008.0(3000

    == X X X

    Q

    Q

    w

    R ;

    QQ R 6.0=Calculate M

    F Ratio;

    M F = X

    OS .. = 151.030005.157

    =0.34 day1 (O.K.)

    5. Design Of secondary clarifier :

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    Total flow of secondary clarifier = Q + RQ=1.6Q= 1.654432=87091.2 m 3 /d

    Take S.O.R. = 20 m 3 / m 2 /day.S.A. = 20

    2.87091 =4354.46Provide 4 Secondary clarifier.

    Surface area of each clarifier= 1088.64 m 2

    1088.64= 24 d

    ;

    d= 37.23 m 37.5 m.S.W.D.= 3.5 mWeir loading rate = d

    Q 4 ;

    = 5.37450112

    ;=115.5

    Q Peak =1.36 m 3 /secS.O.R. = A

    Q ;

    = 25.374

    4

    8640036.1

    ;

    =26.59W.L.R. = D

    Q

    ; =

    5.3748640036.1

    =249.35m

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    2)Excess sludge generated for activated sludgeprocess

    =1696.2kg/day

    3) Volume of primary sludge =4.46 m 3 /hr=107.04 m 3 /day.

    4)Volume of excess sludge generated fromactivated sludge

    process Q w =169.62 m 3 /day.5)Total volume of raw mixed sludge

    =169.62+107.04

    =276.66 km 3 /d6)Total quantity of raw mixed

    sludge=3946.32+1696.2=5642.

    5 kg/d7)Suspended solid cone of raw mixed sludge =

    66.27652.5642

    =20.39 kg/m 3

    8)Approximate % of volatile matters in mixedsludge=70%

    0.7 ..sludgeActivated8.0

    S A P P

    s

    s

    ++

    ( ) ( )

    2.169632.3946

    1696.20.832.39467.0

    ++

    0.73 73%9)Quantity of volatile matters in raw mixed sludge

    is

    =0.73 55642.52

    =4035.46 kg/day

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    10)Quantity of non volatile matter = 100-73%=27%

    0.275642.52=1523.48 kg/day.

    7.Design of Low Rate sludge:.1)Approximate % of destruction of V m =50 %( Designvalue).2)For achieving 50% of volatile matter destruction

    under mesophilic condition the hydraulic retentiontime required is 40day (manual).3)Quantity of Vm in digestive sludge=0.54119.0396

    =2059.51 kg/day.4)Total quantity of non volatile or inorganicindigestive sludge is 1523.48 kg/day.5)Total quantity of solid in digestive sludge

    =2059.51+1523.48=3582.99 Kg/day.6)% of volatile matter in digestive sludge = 99.3582

    51.2059

    =57.48%7)% of inorganic matter = 99.3582

    48.1523 =42.51%8)Depending upon frequency of sludge withdrawn

    consistency of

    digestive sludge from low rate digestion is excepctedto be inrange of 4-6%% consistency = 10000 kg/day

    =10kg/m 3 .

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    9)For an average consistency of 5%(50kg/day)volume of digestive

    sludge is 365.715099.3582

    m= /day,

    10)Volume of digester:V= ( ) 13

    2T V V V d f f ;

    check = 40 ( ) 65.7166.27632

    66.276 ;=5427.06 m 3 .

    8.Check for volatile solids:

    Loading rate kg VSS/daym 3 .

    = 06.5427 039.4119 =0.74 kg VSS/daym 3 .9.Design for gas generation:

    1)Gas generation /kg of volatile matter destroyed =0.9 3 /kg

    2)Total gas generation 0.92059.51.73=1853.559 m3 .

    3)To avoid foaming minimum surface area requiredto meet condition 9 m 3 of gas generated/ day.Per m 3 surface area will be = 9

    559.1853 =205.951 m 2 .4)For operational flexibility and construction reasonsit is suggested to install 2 digester of followingdimensions = 2

    06.5427 ; =2713.53 m3

    5)Minimum surface area = 2951.205 ; =102.97 m 2 .

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    Choosing digester shape as low for vertical cylinderand for Q of 30m the surface area of each digestion= ( )2304

    ; =706.8 m 2 .

    Effective digester depth = m AV

    8.36.141306.5427

    == o f depth.Addition volume of sludge storage during monsoonperiod when sludge drying bed option is not use forsludge dewatering =VdT 2 For a period of 12 day=35.25512;

    =423.06 m 3 ;Equivalent to 8.706

    06.423 =0.59 m;

    Addition allowance for grit and slump accumulation is0.6m free board 0.6 total addition =3.8+0.59+0.6+0.6=5.59 5.6m

    10. Design of sludge drying bed:

    1. Volume of digested sludge= 71.65 daym3

    ;

    2. Dewatering, drying and sludge removalcycle=10 days.

    3. Depth applical of sludge solution= 0.3m

    4. Total plan area of sludge drying=3.0

    1065.71

    = 2388.33= 23.88 m 2

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    Provide 50m long and 10m width of sludge drying bed No. of bed required =

    50033.2388 ;

    =4.77 say 5bedsBed provide with single with singledischarge 5% slope for collection of super native sludge.