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298 94 307/02 Untersuchungen zum Stand der Umsetzung des ...

298 94 307/02 Untersuchungen zum Stand der Umsetzung des ...

298 94 307/02 Untersuchungen zum Stand der Umsetzung des ...

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Teil 3 Seite 10-11<br />

that is formed during the dehydration of fermenter outflow, as well as the elementary sul-<br />

phur that is formed during de-sulphurisation are channelled into thermal conver-<br />

sion/disposal. The stripped ammonia is subsequently catalytically oxidised into nitrogen.<br />

Through the discharge of the ammonia stripper, the volume of water to be transported<br />

outwards is significantly lower compared to animal meal production.<br />

Operational data Applicability<br />

Example for the results of the biogasproduction with matrial out of the Highpressuretem-<br />

peraturehydrolysis<br />

COD value<br />

load<br />

COD reduc-<br />

tion<br />

COD filtrated<br />

reduction<br />

Methane<br />

content in the<br />

bio gas<br />

[kg/m³*d] [%] [%] [%] [m³/Mg]<br />

Biogas recovery<br />

~ 10 80 - 90 85 - 93 70 - 77 ~ 200 - 300<br />

Economics<br />

One tonne of raw material from the animal carcass processing sector yields between<br />

200 and 300 m³ of biogas with an average methane content of above 70%. At an electrical<br />

efficiency rate of 38%, 610 to 780 kWh/t of electrical energy are produced. If the electricity<br />

is fed into the network in accordance with the Renewable Energy Law, the return is € 0,06<br />

to 0,1 per kWh. This works out to € 36,6 to 78 per tonne. The costs for a currently required<br />

production of animal meal, including the high energy consumption involved in the drying of<br />

animal slurry and subsequent incineration can be saved. Only the consi<strong>der</strong>ably lower<br />

quantities of mechanically dehydrated fermentation remnant needs to be dried. A feasibil-<br />

ity study shows that, in comparison to animal meal production and subsequent incinera-<br />

tion, a cost advantage of approx. € 50 can be attained in terms of thermal high pressure<br />

hydrolysis.<br />

The higher energy input during solubilisation has the consequence that the overall pro-<br />

teins and fats are solubilised for biogas conversion. Pre-acidification, which would other-<br />

wise take 15 days with this material, is therefore not required. In contrast to a conventional<br />

biogas plant, in which e.g. category 3 material can be co-fermented in accordance with<br />

the EU ordinance, a time reduction of 40% is achieved for this process.<br />

Driving force for implementation<br />

Compared to conventional process preconditions for category 1 material (133°C, 3 bar<br />

and 20 min.) this results in the advantage that, per tonne of raw material, 600 kW is re-<br />

tained. It has been established that at conventional block type thermal power stations the<br />

ratio of electrical energy to heat is approximately 1:1. However, the heat resulting from<br />

this is known to be difficult to utilise.<br />

Example plants<br />

St. Erasmus animal carcass conversion plant (technical college plant with 1000 kg/h)<br />

Reference literature

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