152 BIOLOGICAL TREATMENT OF WASTEWATER
E. In recent years, several wastewater treatment plants
have been designed to operate with pure oxygen instead
of conventional use of air in activated sludge treatment
process. The obvious advantage of pure oxygen aeration
is the higher oxygen concentration gradient maintained
within the liquid phase, and this condition permits
higher concentration of biomass in the aeration tank.
This process has been shown to be more economical
due to less energy requirements and in some cases has
produced a better quality effl uent. Signifi cant increase
in volumetric loading rate, reduction in sludge produc-
tion, elimination of foaming problems and decrease in
treatment costs are claimed to be advantages.^40
A pure oxygen activated sludge system developed by
Union Carbide Corporation is shown in Figure 18. This
process is operated at MLSS values between 3000–
10000 mg/L and the settling rate of sludge is consider-
ably improved.
F. Extended Aeration
Extended aeration plant is the one where the net
growth rate is made to approach zero, i.e., rate of
growth becomes approximately equal to rate of decay.
This is achieved by increasing the aeration time in order
to keep the sludge in the endogenous growth phase for a
considerable time. In practice, it is impossible to operate
an extended-aeration system without sludge accumula-
tion, because certain volatile solids, mainly polysaccha-
rides in nature and inert organisms in activated sludge
process, accumulate in the plant. Excess sludge is not
generally wasted continuously from an extended aera-
tion, but instead, the mixed liquor is allowed to increase
in suspended solids concentration and a large volume
of the aeration tank content or return sludge is periodi-
cally pumped to disposal. Oxidation ditch plants are
designed and operated on this principle. Layout of a
typical extended-aeration plant and variation in BOD in
aeration tank are shown in Figure 19.
G. Aerated Lagoons
These are similar to the activated sludge system but
without recirculation of sludge. Mechanical or diffused
aeration devices are used for supplying oxygen and also
providing sufficient mixing. All suspended solids may
or may not be kept in suspension, depending upon the
degree of mixing. Deposited solids may undergo anaer-
obic decomposition. Mathematically, the BOD removal
rate in aerated lagoons is given by Eq. 13 and assuming
the aerated lagoon to be a completely mixed system,
without recycle and maintaining sufficient turbulence,
SECONDARY
SETTLING
TANK
EFFLUENT
EFFLUENT
INFLUENT
AERATION BASIN
RETURN SLUDGE
EXCESS SLUDGE
PRIMARY
SETTLING
TANK
INFLOW
SLUDGE
DISPOSAL
BOD
TIME
FIGURE 17 Complete mixing activated sludge.
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