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1) Waste should be avoided. To a certain extent it is possible to
avoid general household waste, however "municipal sewage sludge"
cannot be "avoided", as required by this guideline.
2) If waste cannot be avoided, the priority should be to utilise
the substances it contains. In the case of municipal sewage sludge,
the only practical uses are in the agricultural sector - as organic
fertiliser to improve the soil and for recultivation. If municipal
sewage sludge is to be used in this sector
however, it must meet the following two criteria:
· The sludge must meet the minimum requirements for agricultural
use, i.e. in practical terms the heavy metal concentrations and
also the organic pollutants, such as dioxines and furanes, must not
exceed certain maximum levels.
· A market should be available for the "organic fertiliser", i.e.
there must be a demand for the substance in the immediate vicinity
or a demand must be created for it. The main criterion here is that
this demand be long-term, thus ensuring that there is a means of
disposal available for the waste. Those who know what havoc can be
caused by false information being propagated on television or in
the newspapers will hardly expect to
find a "reliable long-term solution".
If a truly safe means of disposal by utilisation is to be found,
the best possible scenario can only be a combination of "material
utilisation" for as long as possible and "thermal use", as required
in the next step described below.
3) If the "material utilisation" described above is not possible,
the law requires "thermal use". This does not mean that the organic
waste should be destroyed by heat, but that it should be processed
to make solid fuel and then used in place of a primary energy
source. The idea behind this regulation is to reduce CO2 emissions.
4) The final stage for organic waste is dumping, but not until the
organic content has been reduced to less than 5%, which is
generally when it has been well incinerated. When dealing with
municipal sewage sludge, the regulations clearly require that the
sludge be dried after dewatering. Relatively safe use in
agriculture and also proper thermal use is only possible if the
sludge has been dried, normally to a dry solids content of 90 to
95%.
Technical performance of Solid waste drying machine for sale:
Size(m) | Capacity(t/d) | Inclination(%) | Supports(pc) | Damper Type | Kiln Rotation Speed | Main Drive | Auxiliary Drive | |||
Main Drive(r/m) | Auxiliary Drive(r/m) | Motor Power(KW) | Reducer (Overall Ratio) | Motor Power (KW) | Reducer (Overall Ratio) | |||||
φ2.8/2.5×44 | 300 | 3.5 | 3 | Mechanical | 0.445-2.22 | 4.75 | 55 | 49-63 | 4 | 40.44 |
φ3×48 | 600-700 | 3.5 | 3 | Mechanical/ Hydraulic | 0.676-3.38 | 9.36 | 100 | 50 | 7.5 | 14 |
φ3.2×50 | 1000 | 3.5 | 3 | Hydraulic | 0.36-3.57 | 6.5 | 160 | 40 | 15 | 31.5 |
φ3.3×50 | 1200 | 4 | 3 | Hydraulic | 0.36-3.57 | 5.61 | 160 | 40 | 11 | 31.5 |
φ3.5×54 | 1500-1800 | 4 | 3 | Hydraulic | 0.39-3.9 | 7.66 | 220 | 28 | 18.5 | 45 |
φ4×60 | 2500 | 4 | 3 | Hydraulic | 0.41-4.07 | 8.2 | 315 | 22.4 | 22 | 45 |
φ4.3×64 | 3500 | 4 | 3 | Hydraulic | 0.4-4.0 | 7.93 | 400 | 31.5 | 30 | 45 |
φ4.8×74 | 5000 | 4 | 3 | Hydraulic | 0.35-4 | 8.52 | 630 | 42.226 | 55 | 28 |
φ5.0×74 | 6000 | 4 | 3 | Hydraulic | 0.35-4 | 7.58 | 710 | 28 | 55 | 45 |
φ5.6×87 | 8000 | 4 | 3 | Hydraulic | Max4.23 | 8.7 | 800 | 23.901 | 90 | 35.795 |
φ6.0×95 | 10000 | 4 | 3 | Hydraulic | Max5 | 9.2 | 950×2 | 26.646 | 132 | 35.795 |