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identification, assessment and prioritisation of eu ... - Ariacube

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BiPRO<br />

Air emissions seem to be dominated by pesticide use <strong>and</strong> metal industry (predominantly nonferrous<br />

metal production); other sources are chemical industry <strong>and</strong> residential combustion.<br />

Releases to water are due to chemical production but are low in comparison.<br />

Releases <strong>of</strong> PAHs are in another dimension than releases <strong>of</strong> other POP. Based on available<br />

data overall roughly 3000 tons <strong>of</strong> UNECE PAHs (Sum 4) are emitted unintentionally per year<br />

with about 2000 tons being emitted to air <strong>and</strong> roughly 900 tons being discharged to water.<br />

Air emissions seem to be dominated by residential combustion, road transport <strong>and</strong> wood<br />

preservation, however all other sources also contribute with almost one third <strong>of</strong> the total.<br />

Except <strong>of</strong> refinery <strong>and</strong> anode production industrial sectors are no major sources for PAH<br />

releases. Releases to water are related to marine activities mainly.<br />

Detailed results on the source inventory are provided in chapter 5. Information on major data<br />

sources is given in chapter 4.<br />

Inventory <strong>of</strong> measures related to POPs<br />

The inventory <strong>of</strong> measures has been based on Member State answers to a questionnaire,<br />

evaluation <strong>of</strong> available NIPs <strong>and</strong> draft NIPs, literature search <strong>and</strong> an investigation <strong>of</strong><br />

European legislation.<br />

To differentiate <strong>and</strong> evaluate the results the investigation has been performed in the 9<br />

categories: existing legislation, review <strong>of</strong> legislation, planned new legislation, implementation<br />

<strong>and</strong> enforcement <strong>of</strong> existing legislation (administrative, technical), new approaches (economic<br />

incentives, eco-labelling, taxes, subsidies, etc), funding, communication/education,<br />

monitoring/inventory <strong>and</strong> research.<br />

Based on the investigated sources it can be stated that with respect to legislation a range <strong>of</strong><br />

efficient instruments is in place for all releases pathways targeting on general release<br />

reduction or specific reduction <strong>of</strong> POP releases.<br />

The major instruments for release control from industrial sources <strong>and</strong> for reporting on POP<br />

releases are the IPPC Directive, the EPER Decision <strong>and</strong> the E-PRTR regulation.<br />

Other legal instruments are the LCP directive 2001/80/EC, the Waste Incineration Directive<br />

2000/76/EC, the ambient air Directive 96/62/EC <strong>and</strong> its 4 th daughter directive (2004/107/EC),<br />

the Emission Ceiling Directive (2001/81/EC) <strong>and</strong> the Energy Efficiency Directive 2002/91/EC<br />

addressing releases to air. Directive 76/464/EEC <strong>and</strong> the Water Framework Directive<br />

2000/60/EC are the major instruments for monitoring <strong>and</strong> release control to the aquatic<br />

environment. The PCB Directive 96/59/EC, Directive 76/769/EEC <strong>and</strong> Directive 98/70/EC<br />

have addressed the issue from the input side by restricting (banning) production <strong>and</strong> use <strong>of</strong><br />

POPs or substances releasing POP during their lifetime or during disposal/recovery<br />

operations. With respect to releases from waste Directive 75/442/EEC <strong>and</strong> the L<strong>and</strong>fill<br />

directive (1999/31/EC) with all related legislation as well as the EU POP regulation constitute<br />

an effective legal framework.<br />

page 10

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