Activited Sludge Personal
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Basin Volume V 2400 m3
Dry sludge [A] 4 Kg/m3
Cell death rat Kd 0.06 l/day
Substract utili A 0.6
Input stream V 10 m3/min
0.166666667 m3/sInput stream1[BOD] 135 mg/l
1.35E+11 Kg/m3
Input stream2[BOD] 200 mg/l
0.2 Kg/m3
out put strrea [BOD] 15 mg/l
0.015 Kg/m3
out put strrea [BOD] 20 mg/l
0.02 Kg/m3
b)
[B]T1 0.015 kg/m3
[B]1 0.135 kg/m3
[B]T2 0.020 kg/m3 Solver
[B]2 0.200 kg/m3 Left -0.0018
[B]eq 0.005 kg/m3 Right -0.0018
V 2400 m3V 0.1667 m3/s
TB 14400 s 4 h
vB -1
[A] 4 kg/m3
k 0.000208333 m3/kgs
vA 0.6
vad -1
kd 0.06 1/day
kd 6.94444E-07 1/s
TA1 1800000 s 500 h
TA2 847059 s 235 h AA
BBK
1
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c) [A] 6.167 kg/m3
TA 500 h
d) V 1200 m3
TB 7200 s 2
[B]T1 0.02357143
TB 7200
TA1 614634 171
[B]T2 0.00765306
TB 7200
TA2 -2756250 -766
dAdeq k
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eq
B BB
BB
Ak ][][
][][
][
1 0
0
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Given data:
Basin Volume
CSTR 1 VB1 4000 m
CSTR 2 VB2 2000 m
initial input stream Vdotini 250 m/h
Concentration of biomass [A] 4 kg/m
Cell death rate per day kd 0.025 1 /day
Substrate utilisation vA 0.6
vad -1
vB -1
Biological Oxigen Demand [B] 600 mg/l
BOD of CSTR 1 [B] t1 35 mg/l
BOD of CSTR 1+2 [B] t2 27 mg/l
b) residence time CSTR 1 B1 16 [h]
residence time CSTR 1+2 B2 24 [h]
[B]eq 1.0301E-02 Kg/m
[B]eq 10.301 mg/l
K 0.357 m/(kg*h)
h s
c) For CSTR 1 4000m A 235.0 8.46E+05
For CSTR 1+2 6000m A 393.8 1.42E+06
d) Big ==>Small
initial input stream Vdot
ini 250 m/h
Volume of 1st
Reactor VR1 4000 m
Volume of 2nd
Reactor VR2 2000 m
Small ==>Big
initial input stream Vot
ini 250 m/h
Volume of 1st
Reactor VR1 2000 m
Volume of 2nd
Reactor VR2 4000 m
There is no different if stream passes the small basin first, the outlet BOD
refer cre levenspiel
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0212
B
BBB
100
Beq
10
1
BCSTR
q
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[A] 4 kg/m
vb -1
vadd 0
vA 0.6
vad -1
kd 0.025 1/d
B) V flow V flow V [B] [B] [B]T [B]T
m/h m/s m mg/l kg/m mg/l kg/m
250 0.069444 4000 600 0.6 35 0.035
250 0.069444 6000 600 0.6 27 0.027
1/K 10072.13115
K 9.92839E-05
0.010300546
C)
V TA TB
m3 s s
4000 846022 57600
6000 1417555 86400
D) If it Passed through in series
First 4000 then 2000 First
As before the outlet of the first basin is the same so For
[B]1 0.035 kg/m TB1
TA1 846022 s [B]1
TB1 57600 s TA1
For 2000 m3 For
TB2 28800 s [B]2
[B]2 0.012286 kg/m TA2
TA2 -5846175 s TB2
No difference space time remains the same in total
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TB x axis values
s -
57600 2.45226E-06
86400 1.65799E-06
2000 then 4000
2000 m3
28800 s
0.057713568 kg/m
394468.5025 s
4000 m3
0.012286432 kg/m-5846174.77 s
57600
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
1.0E-06 1.5E-06 2.0E-06 2.5E-06
[B]T
Chart Title
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3.0E-06
Series1
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Given Data
V,react = 4000 m
T = constant
[A] = 4 kg / m
kd = 0.025 1 / d
0.00104 1 / hv,A = 0.6 substrate utilisation
v,B = -1
Permitted limit = [BOD] 40 mg / l
0.04 kg / m
a)
b)
V, m / h [B]o(mg/l) [B]mg/l [B]
okg/m
1996 162 680 26 0.68
1999 168 608 25 0.608
2000 228 612 31 0.612
2001 267 604 34 0.604
slope = 1 / k = 2.7245
intercept = [BOD]eq = 0.0082
k = 0.3670 m / (kg * h)
[BOD]eq = 0.0082 kg / m
c)
volume basin 4000 m
[B]o
600 mg / L
0.6 kg / m
[B] 40 mg / L
0.04 kg / mB 12.00 h
V 333.46 m/h
d)
V
VB
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[B]o
600 mg / L
0.6 kg / m
for [B] 40 mg / L
Volume basin 2000 m
B 2.26 h
Required
[B]1, kg/m [B]2, kg/m [B]2, kg / m Diff V (m / h)
0.15 0.04 0.04 1.9791E-09 886.01
V
VB
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[B]kg/m B (h)([BOD] - [BOD]
o)/
vB*[A]*B
0.026 24.69 0.0066
0.025 23.81 0.0061
0.031 17.54 0.0083
0.034 14.98 0.0095y = 2.724
R =
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
0.0000 0.0020 0.0040
V
V
B
eq
BB
o
B
B BOD
A
BODBOD
k
BOD
1
eq
B
BBB
BB
Ak ][][
][][
][
1 0
0
oB BODBOD 1
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eqBBB
Ak
1][
][][][][
Ak
BBAkB
BB
eq
BB
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x + 0.0082
0.9973
0.0060 0.0080 0.0100
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V,react = 4000 m
T = constant
[A] = 4 kg / m
kd = 0.025 1 / d
0.001041667 1 / h
v,A = 0.6substrate
utilisation
v,B = -1
Permitted limit = 40 mg / l0.04 kg / m
V, m / h [B]o, mg/l [B]t, mg/l [B]o, kg/m [B]t, kg/m
1996 162 680 26 0.68 0.026
1999 168 608 25 0.608 0.025
2000 228 612 31 0.612 0.031
2001 267 604 34 0.604 0.034
Slope 2.7245265980.0100
Improvement of an activated sludge system
Into an industrial activated sludge system of 4000m (CSTR basin) the volume flow of
concentration has decreased (long duration average values):
volume flow inlet concentration outlet concentra
1996 162m/h 680mg/l 2
1999 168m/h 608mg/l 2
2000 228m/h 612mg/l 3
2001 267m/h 604mg/l 3
Your task is to predict the maximum volume flow related to the permitted limit of 40mg/l
a) without any change in the process and
b) when the basins will be divided in two parts of 2000m each and passed in ser
Assume a multi-component substrate and ideal CSTR conditions in all basins. The conce
basins is to be estimated to 4kg/m and the normal cell death rate to 2,5% per day (kd= 0,
= 0,6). The temperature in the system is constant!
b) Calculate the equilibrium concentration of BOD [BOD]eqand the rate constant k
(graphical solution possible)! The linearized form of the equation for residence ti
eq
BB
o
B
B BOD
A
BODBOD
k
BOD
1
Draw an adequate diagram!
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Intercept 0.008202071
K 0.3670 m / (kg h)
[BOD]eq 0.0082 kg/m3
Inlet [ ] 600 mg/l
0.6 kg/m3
Outlet [ ] 40 mg/l
0.04 kg/m3
12.00 h
Max volume 333.46 m3/h
Volume Basis 2000 m3
4000 m3
Inlet [ ] 600 mg/l
0.6 kg/m3
Outlet [ ] 40 mg/l
0.04 kg/m3
2.26 h
Volume flow 886.00 m3/h
y = 0.366x -
R = 0.99
0.0000
0.0010
0.0020
0.0030
0.0040
0.0050
0.0060
0.0070
0.0080
0.0090
.
0 0.01
c) Calculate for the 4000m basin the maximum volume flow for an estimated inlet
limit of 40mg/l using the two coefficients from b) or take the value from the dia
d) Calculate (iteration) for the two 2000m basins in series the maximum volume f
600mg/l and an outlet limit of 40mg/l using the two coefficients from b)!
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Outlet
concentration B1
[kg/m3]
Outlet
concentration B2
[kg/m3]
Final
concentration
required [kg/m3]
Difference
0.145379 0.040 0.04 0.000
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Residence
timeBig Equation
24.69 0.0066
23.81 0.0061
17.54 0.0083
14.98 0.0095
astewater has increased, while the outlet
tion
6mg/l
5mg/l
1mg/l
4mg/l
in the outlet
ies.
tration of biomass (dry sludge [A]) in the
25d-1
). The substrate utilisation is 60% (A
from the given data by linear regression
me is
11 points
eq
BB
o
B
B BOD
A
BODBOD
k
BOD
1
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0.003
73
0.02 0.03 0.04
Big Equation
Linear (Big Equation)
concentration of 600mg/l and an outlet
ram!
4 points
eq
B
BBB
BB
Ak ][][
][][
][
10
0
low for an estimated inlet concentration of
6 points
eq
B
BBB
BB
Ak ][][
][][
][
10
0
1][
][][][][
Ak
BBAkB
BB
eq
BB
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V,react 4000 m
T constant
[A] 4 kg / m
kd 0.025 1 / d
0.00104 1 / h
v,A 0.6 substrate utilisation
v,B -1
Permitted limit 40 mg / l
0.04 kg / m
a)
b)
V, m / h [B]o(mg/l) [B]mg/l [B]
okg/m [B]kg/m
1996 162 680 26 0.68 0.026
2001 267 604 34 0.604 0.034
Slope = 1/K 2.76804636
[B]eq 0.007671 kg / mk 0.3613 m / (kg * h)
c)
[B]omg/l [B]
okg/m tB (h) V (m/h)
580 0.58 11.56 346.06
600 0.6 11.99 333.70
620 0.62 12.41 322.19640 0.64 12.84 311.45
d)
BB
B
B
A
BODBOD
k
BOD
1
eq
B
BBB
BB
Ak ][][
][][
][
1 0
0
V
VB
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V,each 1330 m
V,total 3990 m
[B]t 0.04 kg / m
V, m / h t,B, h [B]2, kg/m [B]1, kg/m [B]0, kg/m
800 1.66 0.1177 0.3819 1.2811
1000 1.33 0.1021 0.2837 0.8142
1200 1.11 0.0918 0.2265 0.5769
V
VB
kBB ][][ 0
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600
700
800
900
1000
1100
1200
1300
0.0000 0.5000 1.0000 1.5000
Volumeflow,m/h
Inlet concentration, kg/m
Volume flow vs. Inlet concentration
First Basin
Second Basin
Third Basin
eqBB BBA ][][][ 0
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T constant
[A] 4 kg / m
kd 0.025 1 / d
0.00104 1 / hv,A 0.6
v,B -1
[BOD] 20 mg / l
0.02 kg / m
a)
b)
V, m / h [B]o(mg/l) [B]mg/l [B]
okg/m [B]kg/m B (h)
([BOD] -
[BOD]o)/
vB*[A]*B
160 680 20 0.68 0.020 0.00 #DIV/0!
180 600 20 0.6 0.02 0.00 #DIV/0!
220 580 20 0.58 0.02 0.00 #DIV/0!
slope = 1 / k = #DIV/0!
intercept = [BOD]eq = #DIV/0!
k = #DIV/0! m / (kg * h)
[BOD]eq = #DIV/0! kg / m
substrate utilisation
eq
BB
o
BB BOD
A
BODBOD
kBOD
1
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Given Data
V,react 5000 m
T constant
[A] 4 kg / m
kd 0.025 1 / d
0.00104 1 / h
v,A 0.6
v,B -1
Permitted limit = [BOD] 20 mg / l
0.02 kg / m
a)
b)
V, m / h [B]o(mg/l) [B]mg/l [B]
okg/m
1995 220 580 30 0.58
1998 250 520 32 0.52
2001 270 510 33 0.51
2004 300 470 35 0.47
slope = 1 / k = 7.9484
intercept = [BOD]eq = -0.0174
k = 0.1258 m / (kg * h)
[BOD]eq = -0.0174 kg / m
c)
Total
volume basin 5000 m V
[B]o
400 mg / L volume basin
0.4 kg / m B
[B]2 20.00 mg / L [B]o
0.02 kg / m
B 20.19 h [B]1 = [B]o2
V 247.68 m/h
substrate utilisation
0
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d)
V 272.68 m/h
volume basin 2500 m
B 9.17 h
[B]o
400.00 mg / L
0.40 kg / m
[B]2 0.05695 kg / m
56.95 mg / L
diff [B]2 0.00570 kg / m
5.70 mg / L
with additionally flow
influence of the bypass flow on the outlet concentration
eq
B
BBBAk ][][][ 0
][ k
B
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[B]kg/m B (h)([BOD] - [BOD]
o)/
vB*[A]*B
0.030 22.73 6.05E-03
0.032 20.00 6.10E-03
0.033 18.52 6.44E-03
0.035 16.67 6.53E-03
First
247.68 m/h
2500 m
10.09 h
400 mg / L
0.4 kg / m
0.05125 kg / m
51.25 mg / L
y = 7.9484x - 0.
R = 0.829
0.029
0.030
0.031
0.032
0.033
0.034
0.035
0.036
6.00E-03 6.10E-03 6.20E-03 6.30E
V
V
B
eq
BB
o
B
B
BOD
A
BODBOD
k
BOD
1
101
00
1
AK
BBAKB
BB
eqBB
V
V
B
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1][
][][][
Ak
BBA
BB
eq
BB
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0174
-03 6.40E-03 6.50E-03 6.60E-03
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Given Data
input stram 15.6 m3/min 0.26 m3/sec
T constant
[A] 4 kg / m
kd 0.025 1 / d
0.00104 1 / h 2.89352E-07 1/sv,A 0.6 substrate utilisation
v,B -1
[BOD] 25 mg / l
0.025 kg / m
[BOD] 500 mg/l
0.5 kg/m3
lab
[A] 1000 mg/l
1 kg/m3
y axis x axis
time in minseconds [BOD] in mg/l in kg/m3
30 1800 135 0.135 0.000203 slope 634.17 1/K
60 3600 40 0.04 0.000128 int 0.0064 BOD EQ
120 7200 12 0.012 6.78E-05 K 0.001577 1/s
1440 86400 10 0.01 5.67E-06
Tau A 2142.636312 sTau B 4048.800403 s
Volume of basiin 1052.688 m3
BBOD
dAdeqA
AkBBK
1
eqB
BBB
BB
AKV
V
0
0
1
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0.135
0.01
y = 634.17x + 0.0064
R = 1
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0 0.00005 0.0001 0.00015 0.0002 0.00025
Series1
Linear (Series1)
eq
BB
o
BBOD
A
BODBOD