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Environmental Pollution <strong>and</strong> Management 33<br />

4.3.4 Utilization of waste as raw material <strong>and</strong> fuel <strong>in</strong> cement <strong>in</strong>dustry<br />

Because of <strong>the</strong> special features of <strong>the</strong> cement burn<strong>in</strong>g process - <strong>the</strong> strongly alkal<strong>in</strong>e feed<br />

material, kiln charge <strong>and</strong> kiln dust, oxidiz<strong>in</strong>g kiln atmosphere, temperature distribution <strong>in</strong><br />

<strong>the</strong> burn<strong>in</strong>g system, <strong>and</strong> <strong>the</strong> <strong>in</strong>timate contact between <strong>the</strong> solids <strong>and</strong> gases <strong>in</strong> <strong>the</strong> kiln - it is<br />

possible, on <strong>the</strong> one h<strong>and</strong>, to employ waste materials as fuel <strong>and</strong>, on <strong>the</strong> o<strong>the</strong>r h<strong>and</strong>, to add<br />

waste materials to <strong>the</strong> raw mix or <strong>the</strong> cement. The cement <strong>in</strong>dustry can thus make an<br />

important contribution to <strong>the</strong> disposal of wastes aris<strong>in</strong>g from o<strong>the</strong>r sectors of <strong>in</strong>dustry.<br />

The use of waste materials as “junk fuel” (waste-derived fuel) <strong>in</strong> <strong>the</strong> cl<strong>in</strong>ker burn<strong>in</strong>g process<br />

is subject to limits due to requirements of <strong>environmental</strong> compatibility, product quality, <strong>and</strong><br />

economy <strong>in</strong> relation to primary fuels.<br />

Such materials may be fired <strong>in</strong> a f<strong>in</strong>ely ground condition or <strong>in</strong> lump form. The feed-<strong>in</strong><br />

po<strong>in</strong>ts for <strong>the</strong>se fuels are <strong>the</strong> ma<strong>in</strong> fir<strong>in</strong>g system <strong>in</strong> <strong>the</strong> precalc<strong>in</strong>er or <strong>the</strong> riser duct of <strong>the</strong><br />

cyclone preheater, <strong>the</strong> kiln <strong>in</strong>let or <strong>the</strong> hot gas compartment of a grate preheater kiln, or as<br />

an <strong>in</strong>ter-ground admixture to <strong>the</strong> kiln feed meal.<br />

The kiln <strong>in</strong>let (feed end) can be used for this purpose only <strong>in</strong> plants equipped with<br />

preheaters. The waste-derived fuels fed <strong>in</strong>to <strong>the</strong> system at this po<strong>in</strong>t are mostly <strong>in</strong> <strong>the</strong> form<br />

of coarse lumps. They may consist of scrap motor tires, rubber shreds, shredded<br />

household refuse, compacted refuse, or textile <strong>and</strong> wood wastes. However, f<strong>in</strong>ely divided<br />

waste materials such as acid sludge, low-grade coal <strong>and</strong> oil shale may also be fed <strong>in</strong> here.<br />

As numerous measurements have shown, with proper process control <strong>the</strong> fir<strong>in</strong>g of <strong>the</strong>se<br />

waste-derived fuels does not cause any <strong>in</strong>crease <strong>in</strong> emission of <strong>environmental</strong>ly relevant<br />

pollutants. Emission of diox<strong>in</strong>s <strong>and</strong> furans have received special attention because <strong>the</strong>y<br />

have been identified <strong>in</strong> <strong>the</strong> stack gases from number of solid waste <strong>in</strong>c<strong>in</strong>erators. However,<br />

survey of test results from trial burns at cement kilns <strong>in</strong>dicates that emissions of diox<strong>in</strong>s<br />

<strong>and</strong> furans from <strong>the</strong>se facilities are not significant. When diox<strong>in</strong>s <strong>and</strong> furans have been<br />

observed, <strong>the</strong>y appear to be three orders of magnitude less than those reported for<br />

municipal <strong>in</strong>c<strong>in</strong>erators. Moreover, <strong>the</strong>re is no change <strong>in</strong> diox<strong>in</strong> or furan emissions due to<br />

<strong>the</strong> use of waste-derived fuels. If waste materials with a high sulfur or chloride content are<br />

used as fuels, attention must be paid not only to <strong>the</strong> quality of <strong>the</strong> cl<strong>in</strong>ker <strong>and</strong> cement<br />

produced, but also more particularly to <strong>the</strong> process eng<strong>in</strong>eer<strong>in</strong>g requirements of kiln<br />

control. It is advantageous to carry out an emission prognosis to ascerta<strong>in</strong> what quantities<br />

of waste-derived fuels can permissibly be used.<br />

The waste-derived fuels currently used <strong>in</strong> USA <strong>and</strong> European cement plants are primarily<br />

waste oils <strong>and</strong> spent organic solvents from <strong>the</strong> follow<strong>in</strong>g <strong>in</strong>dustries: pa<strong>in</strong>t <strong>and</strong> coat<strong>in</strong>gs,<br />

auto <strong>and</strong> truck assembly, solvent reclamation, <strong>in</strong>k <strong>and</strong> pr<strong>in</strong>t<strong>in</strong>g, cosmetics, toy, medical <strong>and</strong><br />

electronics. The follow<strong>in</strong>g <strong>environmental</strong> <strong>and</strong> economical benefits can be achieved when<br />

wastes are destroyed <strong>in</strong> a cement kiln:

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