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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 />

3.2.13.3 Solid output<br />

Filter residues arise and require a suitable method of recovery or disposal, e.g. bleaching earth<br />

in edible oil refining or diatomaceous earth in a brewery.<br />

3.2.13.4 Energy<br />

Pumping requires electrical energy.<br />

3.2.14 Membrane separation (C.6)<br />

3.2.14.1 Water<br />

Water is used periodically to clean the separation equipment. The frequency of cleaning and the<br />

volumes of water used vary depending on the product and equipment. Waste water is produced<br />

from washing as well as in the form of separated waste products from the process, and contains<br />

dissolved organic material and SS.<br />

3.2.14.2 Energy<br />

Membrane separation is a pressure driven process, so electrical energy is required. In<br />

electrodialysis, electrical energy is required for the transport of ions.<br />

3.2.15 Crystallisation (C.7)<br />

3.2.15.1 Water<br />

In crystallisation operations, water is used for cooling and is normally recirculated. Depending<br />

on the cooling requirements, water is recirculated via chilling units, cooling towers or cooling<br />

ponds. Waste water containing soluble organic material is generated after the removal of<br />

crystals.<br />

3.2.15.2 Solid output<br />

In the refinery process, active carbon is used if required. Spent active carbon is either<br />

regenerated or disposed of as waste.<br />

3.2.15.3 Energy<br />

Electricity is needed to power the pumps and drives. Energy is needed for the cooling system.<br />

3.2.16 Removal of free fatty acids by neutralisation (C.8)<br />

3.2.16.1 Water<br />

The neutralisation process requires cooling water. The waste water that results from a combined<br />

neutralisation and soap-stock splitting has a temperature of about 100 °C, high acidity and<br />

contains salts of sodium sulphate or sodium chloride and sodium phosphate in high<br />

concentrations. If citric acid is used, this increases the BOD load of the waste water. The<br />

disposal of process waste water with high concentrations of sulphates (>2000 mg/l) into a<br />

MWWTP may cause corrosion of the concrete. Phoshorus levels may be high. The waste water<br />

may also contain FOG.<br />

3.2.16.2 Air emissions<br />

The soap-stock acidulation system may be a source of odour.<br />

130 January 2006 RHC/EIPPCB/FDM_BREF_FINAL

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