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

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

Residual waste treatment and disposal typically have associated with them external<br />

costs. Collection <strong>of</strong> residual waste is typically relatively cheap. Recycling, on the other<br />

hand, can incur higher collection costs, even though the avoided costs <strong>of</strong> treatment /<br />

disposal <strong>of</strong> residual waste may justify the activity from the perspective <strong>of</strong> overall<br />

system costs. Recycling typically implies positive externalities relative to the<br />

production <strong>of</strong> material from primary resources. 679 However, governments rarely<br />

provide subsidies for recycling.<br />

In the absence <strong>of</strong> a high landfill tax and <strong>of</strong> direct pay-by-use (which would directly<br />

deliver the economic stimulus to better manage resources), mandatory recycling can<br />

imply some extra costs for the consumer to fund recycling schemes. Although the<br />

policy does not directly align the costs <strong>of</strong> purchasing goods with the environmental<br />

damage costs, it can force the ‘polluter to pay’ to have their waste recycled.<br />

Contributions made by producer responsibility schemes, and the degree to which they<br />

cover the costs <strong>of</strong> the collection scheme in each individual country will also impact<br />

the overall cost <strong>of</strong> the provision <strong>of</strong> mandatory recycling schemes.<br />

34.10 Evasion and Enforcement<br />

In Switzerland the current producer responsibility schemes that facilitate the majority<br />

<strong>of</strong> recycling are working well. However, if retailers should start to jeopardise the<br />

financing <strong>of</strong> collection via free-riding, the government proposes to introduce a<br />

mandatory charge, as is provided for in the Environmental Protection Law. 680<br />

34.11 Lessons Learned<br />

Denmark<br />

As previously discussed, the 29 % household waste collection rate fell far short <strong>of</strong> the<br />

2000 target <strong>of</strong> 49 % in Denmark despite the minimum recycling standards. According<br />

to Green Alliance, 681 the principle reasons for this shortfall are a lack <strong>of</strong> mandatory<br />

separate collection <strong>of</strong> biowaste and a heavy reliance on bring sites for the collection<br />

<strong>of</strong> glass and paper/cardboard, leading to poor capture rates.<br />

When the government subsequently proposed the kerbside collection <strong>of</strong> paper, the<br />

public voted against it due to the perceived increase in expense to the<br />

679 See, for example, ECOTEC Research and Consulting Limited (2000) Beyond the Bin: The Economics<br />

<strong>of</strong> <strong>Waste</strong> <strong>Management</strong> Options, Report produced for Friends <strong>of</strong> the Earth, UK <strong>Waste</strong> and <strong>Waste</strong> Watch.<br />

Available at http://www.foe.co.uk/resource/reports/economics_waste_options.pdf; D. Hogg (2006)<br />

Impact <strong>of</strong> Unit-based <strong>Waste</strong> Collection Charges, Report for the OECD Environment Directorate, Working<br />

Group on <strong>Waste</strong> Prevention and recycling, May 2006.<br />

680 Federal Office for the Environment (2008) Guide to <strong>Waste</strong> [Online] (Updated 28 th February 2008).<br />

Available at: http://www.bafu.admin.ch/abfall/01472/index.html?lang=en [Accessed 10 th September<br />

2008].<br />

681 Green Alliance (2002) Creative <strong>Policy</strong> Packages for <strong>Waste</strong>: Lessons for the UK, Available at<br />

http://www.greenalliance.org.uk/uploadedFiles/Publications/CPPWDenmark.pdf<br />

561<br />

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

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