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International Review of Waste Management Policy - Department of ...

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many are expected to fall short <strong>of</strong> the 2006 and 2015 targets. 516 A further restriction<br />

to measuring recycling rates is that many Member States have not yet implemented<br />

reliable reporting systems to allow correct measurement <strong>of</strong> how much <strong>of</strong> a vehicle is<br />

recycled or reused. Thus at the moment there are no reliable indicators to measure<br />

the performance <strong>of</strong> the ELV policies, but this will change as reporting increasing.<br />

The cost <strong>of</strong> treating ELVs is closely linked to the price <strong>of</strong> recycled metals, because a<br />

large proportion <strong>of</strong> the recycled material from ELVs will be ferrous or non-ferrous<br />

metal, both <strong>of</strong> which are relatively easy to separate for reprocessing.<br />

The recent collapse in the price <strong>of</strong> recycled metals is a situation that the ELV policies<br />

were implemented to deal with. 517 In many European countries, if the costs <strong>of</strong><br />

recovery exceed the revenue generated from the sale <strong>of</strong> recyclates the differential is<br />

funded by the vehicle producers, and in Japan, Sweden, and the Netherlands by the<br />

levy on all new vehicle registrations. Consequently, the cost to the final owner <strong>of</strong><br />

discarding the vehicle remains zero and illegal dumping is avoided. If the value <strong>of</strong><br />

recovered materials remains low, producers will need to provides additional funds to<br />

support the scheme, and this is likely to increase the cost <strong>of</strong> vehicles, at the margin.<br />

Hence, consumers will likely pay some additional amount for the increased cost <strong>of</strong><br />

recycling ELVs.<br />

GHK, and Bio Intelligence Service (2006) also concluded that the enforcement <strong>of</strong><br />

standards at ATFs increases the quality <strong>of</strong> depollution and quantity <strong>of</strong> recyclable<br />

materials recovered from the vehicle body. Consequently this is a key element to<br />

accruing the potential environmental benefits aimed for following the implementation<br />

<strong>of</strong> the Directive. Therefore, some measure <strong>of</strong> poor performing states can be made in<br />

relation to how many treatment facilities are operating illegally. For example, the<br />

following list shows some indicative figures for the proportion <strong>of</strong> dismantling facilities<br />

that operate illegally in several EU Member States:<br />

442<br />

� France – 40%<br />

� Hungary – 80%<br />

� Poland – 90%<br />

23.6 Implementation Costs<br />

There will be costs involved with preliminary compliance and also with annual charges<br />

for the administration <strong>of</strong> the policy.<br />

For example, in England the preliminary compliance cost assessment estimated the<br />

cost <strong>of</strong> meeting the Directive as £360 to £520 million. This includes a cost to<br />

516 M. Fergusson and IEEP (2006) End <strong>of</strong> Life Vehicles (ELV) Directive: An assessment <strong>of</strong> the current<br />

state <strong>of</strong> implementation by member states, Report for The European Parliament: <strong>Policy</strong> <strong>Department</strong><br />

Economic and Scientific <strong>Policy</strong>,<br />

http://www.europarl.europa.eu/comparl/envi/pdf/externalexpertise/end_<strong>of</strong>_life_vehicles.pdf<br />

517 London Metal Exchange (2009) Steel & Non-Ferrous Metals Prices, Accessed 17 th January 2009,<br />

http://www.lme.co.uk/home.asp<br />

29/09/09

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