Potential amendment E11 – Preparation of scrap metal
Annex II: responses to MS questionnaire
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- ANNEX III: requirements set by the ELV and WEEE Directives, concerning minimisation of environmental impact.
Annex II: responses to MS questionnaireScrap processing installations treating ELV, WEEE and mixed scrap:
Scrap processing installations treating only ELV – Authorized Treatment Facilities and similar facilities without authorisation5
Scrap processing installations treating only WEEE
Scrap processing installations treating only other metal scrap
Shredders, all input material (ktonnes per year) – ELV shredders with information on treated ELV only (data for ELV shredders taken from 5)
ANNEX III: requirements set by the ELV and WEEE Directives, concerning minimisation of environmental impact.ELV Directive (2000/53/EC) ANNEX I Minimum technical requirements for treatment in accordance with Article 6(1) and (3) 1. Sites for storage (including temporary storage) of end-of-life vehicles prior to their treatament: - impermeable surfaces for appropriate areas with the provision of spillage collection facilities, decanters and cleanser-degeasers, - equipment for the treatment of water, including rainwater, in compliance with health and environmental regulations. 2. Sites for treatment: - impermeable surfaces for appropriate areas with the provision of spillage collection facilities, decanters and cleanser-degreasers, - appropriate storage for dismantled spare parts, including impermeable storage for oil-contaminated spare parts, - appropriate containers for storage of batteries (with electrolyte neutralisation on site or elsewhere), filters and PCB/PCT-containing condensers, - appropriate storage tanks for the segregated storage of end-of-life vehicle fluids: fuel, motor oil, gearbox oil, transmission oil, hydraulic oil, cooling liquids, antifreeze, brake fluids, battery acids, air-conditioning system fluids and any other fluid contained in the end-of-life vehicle, - equipment for the treatment of water, including rainwater, in compliance with health and environmental regulations, - appropriate storage for used tyres, including the prevention of fire hazards and excessive stockpiling. 3. Treatment operations for depollution of end-of-life vehicles: - removal of batteries and liquified gas tanks, - removal or neutralisation of potential explosive components, (e.g. air bags), - removal and separate collection and storage of fuel, motor oil, transmission oil, gearbox oil, hydraulic oil, cooling liquids, antifreeze, brake fluids, air-conditioning system fluids and any other fluid contained in the end-of-life vehicle, unless they are necessary for the re-use of the parts concerned, - removal, as far as feasible, of all components identified as containing mercury. 4. Treatment operations in order to promote recycling: - removal or catalysts, - removal of metal components containing copper, aluminium and magnesium if these metals are not segregated in the shredding process, - removal of tyres and large plastic components (bumpers, dashboard, fluid containers, etc), if these materials are not segregated in the shredding process in such a way that they can be effectively recycled as materials, - removal of glass. 5. Storage operations are to be carried out avoiding damage to components containing fluids or to recoverable components and spare parts.
WEEE Directive (2002/96/EC) .ANNEX III Technical requirements in accordance with Article 6(3) 1. Sites for storage (including temporary storage) of WEEE prior to their treatment (without prejudice to the requirements of Council Directive 1999/31/EC): - impermeable surfaces for appropriate areas with the provision of spillage collection facilities and, where appropriate, decanters and cleanser-degreasers, - weatherproof covering for appropriate areas. 2. Sites for treatment of WEEE: - balances to measure the weight of the treated waste, - impermeable surfaces and waterproof covering for appropriate areas with the provision of spillage collection facilities and, where appropriate, decanters and cleanser-degreasers, - appropriate storage for disassembled spare parts, - appropriate containers for storage of batteries, PCBs/PCTs containing capacitors and other hazardous waste such as radioactive waste, - equipment for the treatment of water in compliance with health and environmental regulations
The information below applies for wet scrubber systems of the spray tower type and is taken from [18]. Investment cost: The investment cost to treat a waste gas stream of 10000 Nm³/h with a relatively simple spray tower is 50 000 EUR, being 5000 EUR/1000Nm³. For other capacities a scaling factor to the power of 0.3 can be used. Operational cost personnel cost for maintenance : 0.25 manhour/day operational cost 0.4 – 0.5 EUR/Nm³ additives and residues: the separated dust needs dewatering, transport and disposal. The water needs to be treated before discharge. 1 C. Polders, S. Vanassche en K. Vrancken, Best Beschikbare technieken voor schrootverwerking en sloperijen, final draft, VITO, 2007 2http://www.iiiee.lu.se/Publication.nsf/$webAll/5CF2CB5C4B0A5CCBC1256E8C00461370/$FILE/interim%20report-%20cvr.pdf 3 http://www.efr2.org/html/downloads/scraptrade2006.pdf 4 http://www.efr2.org/html/downloads/presentation.ppt 5 M. Savage et.al. (2006), Implementation of Waste electric and Electronic Equipment Directive in EU-25, EC, DG JRC – IPTS 6 Bio intelligence service et.al. (2006), Gather, process and summarise information for the review of the waste electric and electronic equipment directive, Synthesis report for DG ENV, , 2006 7 DEFRA (2007). Trial to establish waste electrical and electronic equipment (WEEE) protocols. In association with the CIWM (EB), Chartered Institution of Wastes Management Environmental Body 8 GHK, Bio Intelligence Service (2006). A study to examine the costs and benefits of the ELV Directive, report for DG ENV 9 K. Forsgren, StenaMetal, personal communication. 11 COBEREC, comments to Flemish BAT document, august 2007 12 http://glwww.mst.dk/udgiv/Publications/2000/87-7944-295-1/pdf/87-7944-297-8.pdf 13http://www2.mst.dk/common/Udgivramme/Frame.asp?pg=http://www2.mst.dk/udgiv/publications/2003/87-7972-675-5/html/kap05_eng.htm 14 François, F., Blondeel, M., Bernaert, P., Baert, R., ‘Dioxin-like PCB emissions in the Flemish region (Belgium)’, Paper presented at Dioxin 2005, Organohalogen Compounds, 2005, p. 2140 - 2143. 15 http://ec.europa.eu/environment/waste/pdf/end_of_waste.pdf 16 This question looks at whether the design of the option actually addresses the real problem – in the sense of focus rather than effectiveness. Effectiveness issues come after. Hence it is the intention and targeting of the option that is assessed here and not its effect. 17 These installations are shredder installations that perform other treatment processes. They are also included in the figures concerning shredders 18 VITO (2004) Gids Luchtzuiveringstechnieken – LUSS, http://www.emis.vito.be/Luss / VITO and BIO, with Institute for European Environmental Policy and IVM Directory: webdav -> CircaBC -> env env -> Risk Assessment of env -> Member State fact sheet: France Integrated coastal management and climate change adaptation env -> National Summary for Article 12 env -> Natura 2000 Seminars Atlantic Biogeographic Region Case Studies env -> Convention on the conservation of european wildlife and natural habitats env -> Ibuprofen pnec derivation June 2015 env -> Climate change impacts on the water cycle, resources and quality env -> Directorate-general env -> Aquaculture guidance second draft comments and case studies received from ad hoc group Download 0.61 Mb. Share with your friends:
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