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

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According to this paper:<br />

427<br />

� The creation <strong>of</strong> networks <strong>of</strong> dismantlers linked to individual car companies has<br />

been a major organisational innovation given the previously existing limited<br />

relationships between the car industry and post-consumer ELV treatments.<br />

However, contractual arrangements between the main actors (carmakers,<br />

dismantlers, shredders, and recyclers) differ from country to country.<br />

� Innovative developments concerning design for dismantling (DFD) are taking<br />

place in all car companies. DFD may consist <strong>of</strong> small changes in the partassembling<br />

systems or it may imply changes and adaptations <strong>of</strong> components<br />

and parts. The boundaries between DFD and design for recycling (DFR) are not<br />

clear-cut.<br />

� DFR requires definition and measure <strong>of</strong> “recyclability”. European carmakers<br />

work on the development <strong>of</strong> “recyclability coefficients” for materials and<br />

components and include lists <strong>of</strong> not admitted or undesired<br />

substances/materials in the technical specifications imposed to component<br />

suppliers. Thus, a “responsibility transfer” between industries takes place. DFR<br />

is also increasingly linked to Life-Cycle Analysis (LCA). Most carmakers are<br />

investing in recycling-oriented LCA at the research & development (R&D) level<br />

and, in some cases, they are transferring results to practice. LCA is generally still<br />

limited to specific materials or car components. DFR pushes most carmakers to<br />

pursue a simplification <strong>of</strong> the material regime. “Easily” (i.e. economically)<br />

recyclable materials are favoured and, as a consequence, the trend towards the<br />

use <strong>of</strong> certain polymers and composite materials is weakening. There is a<br />

propensity to reduce the number <strong>of</strong> polymers in favour <strong>of</strong> those having the best<br />

recycling possibilities and a process <strong>of</strong> inter-polymer substitution is underway.<br />

The legislation not only transposed into Irish law the EU Directive on End <strong>of</strong> Life<br />

Vehicles (Directive 2000/53), it also made a significant amendment to the <strong>Waste</strong><br />

<strong>Management</strong> (Permit) Regulations 1998. This amendment enlarged the decisionmaking<br />

criteria under which all types <strong>of</strong> waste permit application received since 8<br />

June 2006 are considered 486 .<br />

22.10 Social and Distributional Consequences<br />

The Regulations are designed to allow competition to operate effectively and should<br />

not lead to market distortions, particularly in relation to existing small businesses<br />

operating in the scrap-vehicle dismantling sector.<br />

Each producer is required to establish a national system for the collection and<br />

treatment <strong>of</strong> negative value ELVs for which they are responsible. While the national<br />

network, which a producer puts in place for the collection and treatment <strong>of</strong> ELVs,<br />

must be a minimum <strong>of</strong> 43 ATFs nationally, there is no maximum limit; hence there will<br />

be opportunities for the existing operators to compete for this business.<br />

486 Duncan Laurence Environmental (February 2007) <strong>Waste</strong> <strong>Management</strong> End <strong>of</strong> Life Vehicles<br />

Regulations 2006, Legislation Summary.<br />

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

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