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SO - Rheinkalk

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Thermal waste treatment plants<br />

At the beginning of the 1990s retrofitting or construction of flue-gas cleaning plants<br />

was initiated for municipal waste and hazardous waste incineration plants (MWI /<br />

HWI). The driving force for this was the 17th BImSchV in Germany which was nearly<br />

completely transferred to European legislation, which moreover also affected other<br />

industrial fields.<br />

Important objectives in this respect include high efficiencies in the removal of HCl<br />

and <strong>SO</strong>2 in addition to the already much-discussed ecotoxic pollutants. In order to<br />

meet the mandatory objectives, very complicated wet processes were installed in the<br />

first phase while some operators used retrofitting or upgrading existing semi-dry or<br />

dry processes. The installation of the MCD process proved to be a successful<br />

measure for the cost-effective compliance with the 17th BImSchV. The various<br />

methods include combinations of spray sorption and dry sorption as well as a<br />

combination of two dry sorption steps. Of considerable importance for this is the use<br />

of a highly reactive Spongiacal ® product in the dry sorption stage. The application of<br />

mixed adsorbents is widely used to reduce ecotoxic pollutants.<br />

<strong>SO</strong>2-separation [%]<br />

100<br />

80<br />

60<br />

40<br />

20<br />

0<br />

Schematic description of the MKT-process<br />

one stage spray<br />

dry sorption<br />

Stoichiometric ratio<br />

savings ~ 30 - 50 %<br />

0,0 1,0 2,0 3,0 4,0<br />

Stoichiometric ratio [-]<br />

Graph 5: Description of the MCD process (Two-Stage-Process)<br />

The operating temperatures of the dry sorption stages have recently been used to<br />

optimise operational processes. The temperatures in the fabric filter stage usually lie<br />

between 150 °C and 190 °C. Current investigations have also been carried out at<br />

220 °C.<br />

5

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