civil engineering design
TRANSCRIPT
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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.