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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 7<br />

The risks associated with the use of EDTA have been assessed by the European Chemicals<br />

Bureau [256, European Communities European Chemicals Bureau, 2004]. The report of the risk<br />

assessment refers to the total European market for EDTA and states “A high level of usage is<br />

the dairy and drinks industry, with 50 % of the total reported tonnage”. The report discusses<br />

removal rates for some on-site WWTPs and some MWWTPs. It concludes “There is a need for<br />

limiting the risks; risk reduction measures which are already being applied shall be taken into<br />

account. This conclusion is reached because of the high emissions due to the use of EDTA in<br />

industrial detergents. The exposure near sites within dairy and beverage industry with no<br />

effective EDTA removal in their treatment plants is expected to lead to a risk for aquatic<br />

organisms”. The report then also mentions other industrial sources of EDTA emissions to water.<br />

During the information exchange, the use of EDTA and its emission to water was acknowledged<br />

to be an ongoing problem in the FDM sector. The TWG agreed that it is BAT to minimise the<br />

use of EDTA. Throughout the work, the TWG reported that for some applications there are no<br />

known effective substitutes which can be used to completely eliminate the use of EDTA and<br />

that the effectiveness and environmental impact of some potential substitutes had not been<br />

adequately assessed. During the final TWG meeting, it was reported that EDTA is not used in<br />

dairies in the UK. The possibility of determining BAT to eliminate the use of EDTA could be<br />

greatly helped if information about alternative substances already in use was provided and<br />

research into other alternatives was <strong>und</strong>ertaken, before this document is reviewed.<br />

A number of activities, particularly in relation to vegetable processing, are seasonal. Some<br />

members of the TWG have expressed concern about the application of generic BAT to seasonal<br />

activities, due to different economic standards, although specific information about these<br />

difficulties was not provided. This issue is not well covered in this document. Information about<br />

seasonal activities should be collected in the future.<br />

Some information was provided by the TWG after the consultation period when it was too late<br />

to take it into account. For example, late information was received about enzymatic degumming<br />

of vegetable oils and fats and enzymatic interesterification of fully hydrogenated vegetable oils<br />

and fats. Such information can be consi<strong>der</strong>ed when this document is reviewed. It is<br />

recommended that degumming of vegetable oils be fully appraised when this document is<br />

reviewed. The TWG discussed the use of either citric acid or phosphoric acid, particularly with<br />

reference to their relative impacts on the final phoshorus content of treated waste water and their<br />

economic viability. The TWG did not reach a conclusion about which technique is BAT.<br />

Other issues have been raised during the information exchange, but not fully appraised. It is<br />

recommended that information be provided about these for discussion when this document is<br />

reviewed. These issues include:<br />

• as a general principle, a wi<strong>der</strong> examination of the applicability of techniques reported to be<br />

applied in one sector that could be carried out in other sectors. This would optimise the<br />

opportunity for sectors to learn from each other. For example, pigging was reported for use<br />

in jam making, but it is already widely applied in the FDM sector and may be applicable as<br />

a dry cleaning technique in other FDM sectors, for which it has not yet been consi<strong>der</strong>ed<br />

• identification of more opportunities for by-product valorisation, to optimise the use of food,<br />

drink and milk materials and to minimise waste generation<br />

• economic information about the costs of investing in and operating techniques and the<br />

associated direct and indirect savings, e.g. due to reduced energy or waste disposal costs, or<br />

reduced losses from unintentional losses due to leakage or spills<br />

• identification of BAT associated with high, medium and low pressure cleaning. The TWG<br />

were unable to determine which of these techniques is BAT. Increasing the pressure can<br />

remove solid residues by physical force and potentially reduce the consumption of hot and<br />

cold water and detergents. Increasing the pressure also increases the aerosol levels produced<br />

and this can cause hygiene problems, particularly if it is necessary to carry out cleaning<br />

during production<br />

• although many air abatement techniques are described in this document, there is very little<br />

information about their application and applicability in the FDM sector<br />

620 January 2006 RHC/EIPPCB/FDM_BREF_FINAL

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