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Y
Q
Y
=
(24.64)
obs
1
+
ct
where
Y
obs
= Observed yield in the system with recycle (mg/mg).
Y
= Maximum yield coefficient over finite period of log growth (mg/mg).
Q
ct
= Mean of all residence times based on solids in aeration tank and in secondary clarifier
(days).
24.7.1.13.1 Process Design and Control Relationships
The specific substrate utilization rate (closely related to F/M ratio, which is widely used in practice)
can be computed by
r
X
su
U
=
(24.65)
(
)
=
QS
−
S
SS
X
−
o
o
U
=
(24.66)
VX
θ
The net specific growth rate can be computed by
1
θ
c
=−
YU
K
(24.67)
d
The flow rate of waste sludge from the sludge return line will be approximately
VX
X
Q
=
θ
(24.68)
wt
cr
where
X
r
is the concentration of sludge in the sludge return line (mg/L).
24.7.1.13.2 Sludge Production
The amount of sludge generated per day can be calculated by
P
x
=
Y
obs
Q
(
S
o
-
S
)(8.34)
(24.69)
where
P
x
= Net waste activated sludge (VSS) (kg/day, lb/day).
Y
obs
= Observed yield (g/g or lb/lb).
Q
= Influent wastewater flow (m
3
/day, MGD).
S
o
= Influent soluble BOD concentration (mg/L).
S
= Effluent soluble BOD concentration (mg/L).
8.34 = Conversion factor [(lb/MG):(mg/L)].
24.7.1.13.3 Oxygen Requirements
The theoretical oxygen requirement to remove the carbonaceous organic matter in wastewater for an
activated biosolids process is expressed by Metcalf & Eddy (1991) in SI units and the British system:
Mass of Oper dayTotal mass of BODused
2
=
−
1.42(mass of organismswasted,
P
x
)
u
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