Source:
Lenntech - Wastewater Treatment
Stabilization
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Aerobic stabilization can be
performed simultaneously in an activated sludge plant whereby primary
and secondary sludge are continuously aerated for long periods of time.
In aerobic digestion the microorganisms extend into a respiration phase
where materials previously stored by the cell are oxidized, resulting in
a reduction of the biologically degradable organic matter. Thus, aerobic
stabilization of the entire excess sludge (including primary sludge) is
energy consuming. Additionally, it calls for extra reactor volume. |
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The anaerobic sludge digestion takes place in the highly visible digesters. |
Thickenings
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A volume reduction of approximately 30 – 80 % can be reached with sludge thickening before a further treatment. At smaller wastewater treatment plants, where the sludge is driven off regularly, thickening usually takes place directly in the sludge storage tank. The sludge is compressed at the tank bottom only by the force of gravity, while above the sludge a cloudy water layer is formed, which is taken off and led back into the inlet.
On larger plants
separate thickening basins exist. These basins are equipped with
slow rotating vertical rods, which create micro canals in the sludge
for a better dewatering. Also pure machine thickening is gaining
more significance with e.g. non-stabilised sludges, that could rot
during the storage. |
Dewatering
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A further reduction of the sludge amount is mostly necessary after the thickening. The liquid sludge has to be dewatered and has to conform to a dry and porous form. Dewatering can be done naturally (dry beds, solar drying), however this is only possible during a long period of time. Faster and smaller, but also more cost intensive, are machine processes such as pressing (filter press) and centrifugation (centrifuge).
For a good dewatering,
size and firmness of the sludge agglomerates are important, so that
these remain porous during the compression. Flocculants are often
used to achieve as high as possible drying material contents at the
machine dewatering and must be specifically co-ordinated with the
accruing sludge. |
Drying
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A further reduction of the sludge weight is possible with the help of sludge drying, by evaporating the remaining bound water in the sludge. However a significant reduction of the sludge volume cannot be reached with that method.
Sludge drying
procedures are based particularly on contact-, convection or
radiation procedures. Convection drying obtains its effect by treating the sludge with hot-air. In addition ambient air is heated to a high temperature with a burner or steam heat exchanger and brought in contact with the sludge in a drum or belt dryer. The obvious characteristic of radiation drying is that the warmth, which is necessary for the drying process, is supplied through radiation to the sludge. General examples for warmth supply through radiation are solar radiation or infrared heating elements. For the choosing the suitable drying method one should pay attention to
Because of their high investment and operating costs, sludge drying is mainly used in large wastewater treatment plants. ![]() |
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