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Government in the form <strong>of</strong> additional running costs for the DVLA at £2 million to £7<br />

million per annum. 518 This equates at around £1 - £4 per car currently scrapped in<br />

the UK. An additional fund to cover the increase in abandoned vehicles was also<br />

provided by the <strong>Department</strong> <strong>of</strong> Trade and Industry to help Local Authorities with<br />

increasing clear up costs.<br />

Costs in setting up trade associations and for applying standards for ATFs and<br />

recovered materials can also imply further costs for a State implementing such<br />

policies, as can the cost <strong>of</strong> providing adequate reporting systems so that recycling<br />

targets can be measured, and developing administrative systems to manage CoD.<br />

23.7 Effects on Technical Change / Innovation<br />

The policies should drive manufacturers to design vehicles that are easier to recycle<br />

and recovery materials from. However, GHK, and Bio Intelligence Service (2006)<br />

conclude that, notwithstanding manufacturer’s legal obligation to design vehicles in a<br />

way that they meet the recycling and recovery targets set out in the EU Directive,<br />

there is limited evidence <strong>of</strong> any significant change in vehicle design. This could be<br />

due to:<br />

443<br />

� Historic trends showing that vehicle construction materials are moving away<br />

from ferrous metals to plastics (that are harder to recycle) so industry is taking<br />

time to find novel ways to design new components with recyclability in mind; 519<br />

� The marginal costs <strong>of</strong> recycling replacement components being high, due to<br />

the labour costs involved in manual dismantling; or<br />

� A greater level <strong>of</strong> R&D into post-shredder technologies being undertaken, thus<br />

negating the need for further design improvements to the vehicles to meet<br />

higher targets. Estimates are that new processes could generate capture rates<br />

<strong>of</strong> up to 75% from the ASR. 520 This would allow for the 95% target to be met<br />

with little extra being done above the current 80% baseline. Hence if this is a<br />

more cost effective option than to redesign components to be easily recycled<br />

at the dismantlers, producers may be relying on this technology to meet the<br />

recycling and recovery targets.<br />

As highlighted in Section 23.5.2, marginal recycling and recovery rates are potentially<br />

only achievable if R&D is invested into post-shredder technologies (that can<br />

mechanically sort recyclables from the residue) in order to make further recycling<br />

cost-effective. All the main studies considered in this report indicate that the ELV<br />

518 A. Doran (2003) <strong>Policy</strong> discussion by Andy Doran from LARAC, Accessed 15 th October 2008,<br />

http://www.larac.org.uk/pdf/elvbrief.pdf<br />

519 <strong>Waste</strong> Online (2004) End <strong>of</strong> life vehicle and tyre recycling information sheet, Accessed 15 th October<br />

2008, http://www.wasteonline.org.uk/resources/InformationSheets/vehicle.htm<br />

520 GHK and Bio Intelligence Service (2006) A study to examine the benefits <strong>of</strong> the End <strong>of</strong> Life Vehicles<br />

Directive and the costs and benefits <strong>of</strong> a revision <strong>of</strong> the 2015 targets for recycling, re-use and recovery<br />

under the ELV Directive, Final Report to DG Environment, May 2006,<br />

http://ec.europa.eu/environment/waste/pdf/study/final_report.pdf<br />

<strong>International</strong> <strong>Review</strong> <strong>of</strong> <strong>Waste</strong> <strong>Policy</strong>: Annexes

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