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Integrierte Vermeidung und Verminderung der Umweltverschmutzung

Integrierte Vermeidung und Verminderung der Umweltverschmutzung

Integrierte Vermeidung und Verminderung der Umweltverschmutzung

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Chapter 3<br />

While the overall water used is about 15 m 3 /t sugar beet processed, the consumption of fresh<br />

water is 0.25 – 0.4 m 3 /t sugar beet processed, or even less in mo<strong>der</strong>n sugar factories. Water<br />

consumption depends on the activities of each installation, e.g. more water is consumed in an<br />

installation that extracts and refines sugar beet, than one that does only one of those activities.<br />

In Austria, the consumption of water is of 1.5 m³/t of sugar beet processed, equivalent to<br />

9 m³/t produced sugar, was reported [152, Austria, 2002]. Table 3.69 shows the water<br />

consumption in Danish sugar factories.<br />

Parameter Specific value<br />

per tonne of beet processed<br />

Specific value<br />

per tonne of sugar produced<br />

Average Range Average Range<br />

Water (m 3 ) 0.37 0.23 a – 0.50 b 2.39 1.56 a – 3.21 b<br />

a Excluding cooling water (two factories)<br />

b Including cooling water (two factories)<br />

Table 3.68: Water consumption in Danish sugar factories<br />

[139, Nielsen E.H. Lehmann, 2002]<br />

3.3.8.1.2 Waste water<br />

Sugar beet is 75 % water, and the extraction process, by definiton, aims to release a high<br />

proportion of water contained in the beets. Approximately half of this water is lost due to<br />

evaporation or inclusion in various product streams. The remain<strong>der</strong> is, after usage for washing<br />

and fluming, a source of high strength waste water.<br />

The beets are floated through the cleaning stage where stones, weeds and other gross<br />

contaminants are removed. The transport water pumped off with the soil sludge can be up to<br />

70 % of the beet. It has a high organic contamination due to the soil and sugar from damaged<br />

beets. Its COD is 5000 – 20000 mg/l.<br />

The beets then enter the installation, where they are washed before being sliced into cossettes to<br />

maximise the surface area for the extraction process. The condensate from the evaporation and<br />

crystallisation stages is partly used as process water in several process stages, including beet<br />

washing. Process waste water is deemed to be the excess condensate from the concentration and<br />

crystallisation stages. This surplus condensate is high in ammonia and relatively low in COD<br />

content. Waste water with high BOD levels is produced in large volumes [13, Environment<br />

Agency of England and Wales, 2000] and is cleaned in a WWTP.<br />

3.3.8.1.3 Solid output<br />

During the reception and fluming of the sugar beet, soil, stones, sand and vegetable matter, e.g.<br />

seeds, beet tails and leaves, are removed. The amount of the earth adhering to the beet may vary<br />

greatly depending on, e.g. the weather conditions during harvesting and the design and<br />

operation of the harvester. In the annual processing of 500000 tonnes of beets, an average of<br />

60000 tonnes of soil accumulates [87, Ullmann, 2001]. The soil arriving at the installation is<br />

removed in settling ponds. The sediment may be re-applied to arable land or may be used for<br />

other purposes, such as horticulture or civil engineering works. The vegetable matter is<br />

separated from the fluming water for sale as animal feed or fertiliser.<br />

The sugar content of the beets does not vary greatly, e.g. 18.4 % in Austria and 13.9 % in<br />

Greece [87, Ullmann, 2001]. The efficiency of sugar extraction is about 90 %. There are other<br />

substances either in the wastes or by-products, such as beet pulp. After sugar is taken out, the<br />

extracted beet pulp is pressed. The wet pulp may then be dried. Beet pulp is normally sold as<br />

sweet feed for cattle. Another by-product is carbonatation lime. Juice purification is done using<br />

lime. It may be pressed and sold to de-acidify or balance the pH of soil.<br />

198 January 2006 RHC/EIPPCB/FDM_BREF_FINAL

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