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

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oth pieces <strong>of</strong> legislation is to restrict, or eliminate, the use <strong>of</strong> hazardous materials in<br />

manufactured goods sold overseas.<br />

22.12 Effect <strong>of</strong> the <strong>Policy</strong> on Pricing <strong>of</strong> Resources / Services<br />

It is difficult to determine the actual costs for the treatment <strong>of</strong> ELVs, however, it has<br />

been estimated to be in the region <strong>of</strong> €60 to €80/vehicle. These costs could accrue<br />

to circa €6.6m annually.<br />

KPMG carried out two studies with a view to determining the appropriate levy to be<br />

paid to authorised treatment facilities for the depollution <strong>of</strong> ELVs. 492 The first report in<br />

May 2002 recommended that a levy be set at €153/ELV excluding VAT; in a<br />

subsequent report completed in 2003 KPMG recommended a revised figure <strong>of</strong><br />

€120/ELV excluding VAT. These figures included the costs <strong>of</strong> depollution. The reports<br />

were based on an analysis <strong>of</strong> the costs and revenues associated with dismantling an<br />

end-<strong>of</strong>-life vehicle, taking account <strong>of</strong> the labour / administration costs. The reports<br />

noted the volatile nature <strong>of</strong> the market for hulks and scrap metal and the<br />

susceptibility <strong>of</strong> this market to price fluctuations. The second KPMG report noted that<br />

there was scope for the price <strong>of</strong> any proposed levy to fall to €60 to €70 per vehicle.<br />

It is reasonable to suggest the manufacturing cost <strong>of</strong> vehicles has been affected by<br />

the specific requirements imposed on vehicle manufacturers. The reduction <strong>of</strong><br />

hazardous components, the labelling <strong>of</strong> components for recycling, design for<br />

dismantling has, most likely, imposed upward pressure on vehicle manufacturing<br />

costs. However, as technologies develop the cost <strong>of</strong> such change may diminish. As a<br />

result <strong>of</strong> the competitive nature <strong>of</strong> vehicle sales and the numerous variables involved,<br />

it is difficult to determine if additional costs have been passed on to the end<br />

user/customer.<br />

22.13 Evasion and Enforcement<br />

It is an <strong>of</strong>fence for an individual or an ATF to fail to comply with the law on the<br />

disposal <strong>of</strong> ELVs. In particular, it is an <strong>of</strong>fence not to obey the rules concerning vehicle<br />

CoD, or not to deposit at an ATF a vehicle intended to discard as waste.<br />

Penalties for <strong>of</strong>fences set out under the <strong>Waste</strong> <strong>Management</strong> Acts apply. On summary<br />

conviction a fine <strong>of</strong> up to €3,000 and/or 12 months imprisonment can be imposed.<br />

For conviction on indictment a fine <strong>of</strong> up to €15,000,000 and/or 10 years<br />

imprisonment is available to the court.<br />

492 <strong>Department</strong> <strong>of</strong> the Environment, Heritage & Local Government (May 2006) Statement on<br />

Regulatory Impact – <strong>Waste</strong> <strong>Management</strong> (End <strong>of</strong> Life Vehicles) Regulations 2006.<br />

429<br />

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

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