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

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kg), and a TV (15 kg), finding the average WEEE cost <strong>of</strong> these products to be<br />

€5.34. 451 In monopolistic environments, the average product had a €6.33 WEEE<br />

charge attached to it, which was found to be more than double the €2.93 charge in<br />

competitive environments. Nonetheless, monopolistic environments may be the best<br />

way to get new infrastructure in place for the more recent WEEE implementation in<br />

some MS.<br />

According to a report by OECD, 452 there is limited evidence to support the effect <strong>of</strong><br />

pricing on the demand for EEE. However, this is difficult to believe. In theory, the<br />

higher product price resulting from WEEE producer responsibility should lead to a<br />

reduction in the quantity demanded, even if only at the margin. The issue, therefore,<br />

is that given the relatively high cost <strong>of</strong> most EEE compared to the average additional<br />

WEEE cost given above (€5.34), it is likely that price increases are too small to have<br />

any significant influence on demand. In addition, even if the elasticity <strong>of</strong> demand was<br />

-0.2, a 5 % increase in price gives at most a 1 % reduction in demand, whilst there<br />

remains an overall rising trend in EEE consumption worldwide. Hence, though<br />

difficult to discern, there probably is a pricing effect on the demand for EEE. However,<br />

this effect is simply very small, owing to the relatively small impact on product prices<br />

and the inelastic nature <strong>of</strong> demand for most EEE items.<br />

20.9 Evasion and Enforcement<br />

The UNU and Greenpeace reports note that there is ‘leakage’ in the current WEEE<br />

system throughout Europe and worldwide, particularly concerning items <strong>of</strong> value such<br />

as large domestic appliances that contain a lot <strong>of</strong> metals, and IT and telecoms<br />

equipment such as desktop computers and mobile phones. WEEE may escape the<br />

proper management system via illegal exports or via back-door sales to unlicensed<br />

operators, both less-equipped to manage WEEE in an environmentally-sound manner.<br />

The UNU report gives the following examples:<br />

399<br />

� Shipments <strong>of</strong> WEEE disguised as goods from Hamburg port (DEUTSCHE<br />

UMWELTHILFE 2007);<br />

� 28 % <strong>of</strong> businesses found to be exporting WEEE illegally from the Netherlands<br />

(VROM 2007).<br />

As discussed previously in Section 20.5, it is estimated that only 25% <strong>of</strong> WEEE<br />

arisings within the EU are currently being collected and treated, with no precise data<br />

available on what happens to the remaining 75%. 453 It is considered to be likely that<br />

some portion <strong>of</strong> this ‘hidden flow’ is being illegally exported to non-EU countries. In<br />

addition, ‘free-riders’ in the system also contribute to the ‘hidden flow, with VROM<br />

451 R. Veit (2005) How do WEEE get it right?, EMSNow, available at<br />

http://www.emsnow.com/npps/story.cfm?id=15184<br />

452 OECD (2006) EPR Policies and Product Design: Economic Theory and Selected Case Studies,<br />

Working Group on <strong>Waste</strong> Prevention and Recycling, Environment <strong>Policy</strong> Committee.<br />

453 Greenpeace (2008) Toxic Tech: Not in Our Backyard, Uncovering the Hidden Flows <strong>of</strong> e-<strong>Waste</strong>.<br />

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

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