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AERATION
TANKS

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The aeration system consists of six adjacent
aeration tanks. Each tank is divided into
four passes called basins; each basin is
300 feet in length, 35 feet wide, 20.85
feet deep. The overall capacity of each
aeration tank is 6.41 MG for a total secondary
capacity of 38.46 MG.
Two air diffusion systems (fine and coarse)
are used to deliver process air to and around
the aeration tanks. The 26,688 fine bubble
diffusers are a porous ceramic disk, which
divide air into fine bubble diffusion, which
is used to supply oxygen to the microorganisms
and provide mixing of the suspended solids
within each aeration tank.
Process air is also delivered to the influent
and effluent channels of the aeration basin
and the influent channel to the final clarifiers.
This process air, known as channel air,
provides coarse bubble diffusion for two
primary reasons: agitation, keeping the
solids in suspension and the addition of
air helps maintain a higher level of DO
keeping the sewage fresh minimizing obnoxious
odors.
During normal operation two flow streams
enter the aeration system, primary effluent
(secondary influent wastewater) and Return
Sludge (RSL) from the final clarifiers,
called return activated sludge. When the
RSL and the wastewater are mix together,
the combination is known as mix liquor and
often referred to as mix liquor suspended
solids (MLSS). The mixed liquor volatile
suspended solids (MLVSS) is an approximation
of the viable microorganism in the system,
which do the actual wastewater purification.
Most organisms in activated sludge are obligate
aerobes; they need free oxygen to stay alive.
The fine bubble diffusers located on the
bottom of the aeration basins provide the
oxygen.
The day-to-day operation of the activated
sludge process involves a variety of activities.
Observations by the operator must be recorded.
Laboratory test must be performed along
with microscopic examination of the activated
sludge. The dynamic, biological system must
be kept alive and operating. Different process
modes of operation are available to meet
different constraints and needs. Methods
for regulating the activated sludge must
be systematically followed. Finally, the
process must be carefully monitored to ensure
proper conditions are maintained and stop
any problems from developing.
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