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

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incentivising producers to set up reuse systems. There is not yet unequivocal<br />

evidence to support this – reuse systems depend on short delivery distances and<br />

repeated reuse to score environmentally over on-way packaging. Allied to this,<br />

policies to encourage a minimum recycled content, such as that in Belgium, in which<br />

containers that are made with more than 50% recycled material are exempted from<br />

the one-way container tax may help to support the recyclate market.<br />

As referred to in the introduction, the other policy to complement producer<br />

responsibility is PBU. Producer responsibility can favour one material type over<br />

another, which PBU cannot. PBU can adjust the marginal cost per tonne <strong>of</strong> waste<br />

management by location, reflecting the differing costs associated with urban or rural<br />

areas.<br />

Other policies which support producer responsibility are policies which make the<br />

costs <strong>of</strong> dealing with residual waste relatively high (landfill / incineration levies and<br />

bans). In these cases, irrespective <strong>of</strong> the distribution <strong>of</strong> costs, there will be incentives<br />

to increase recycling and to prevent waste so as to avoid the high costs <strong>of</strong> residual<br />

waste treatment / disposal.<br />

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

There are a number <strong>of</strong> incremental costs <strong>of</strong> the producer responsibility policy:<br />

248<br />

� Capital equipment (for reuse);<br />

� Storage space (for reuse);<br />

� Information gathering and reporting;<br />

� ‘Marketing’ <strong>of</strong> the service;<br />

� Establishment <strong>of</strong> the institutions;<br />

� Administration overheads; and<br />

� Operation <strong>of</strong> the recycling/recovery (covered by fees).<br />

The cost <strong>of</strong> the policy applied to household packaging can be borne either by the<br />

taxpayer, supporting the work <strong>of</strong> the municipalities, or the packers/fillers/importers,<br />

or shared between the two. If the cost is partially or totally borne by industry, then<br />

depending on the elasticity <strong>of</strong> demand for the product and the commercial conditions,<br />

some or all <strong>of</strong> the cost may be passed onto the end consumer. This can be<br />

considered as another cost <strong>of</strong> production, and the producers<br />

(packers/fillers/importers) can reduce it effectively, for example by lightweighting,<br />

material switching or alternative logistical processes.<br />

One report identified the so-called financing need <strong>of</strong> different systems and suggested<br />

that for the German system, this is far greater than that in the UK, France or the<br />

Netherlands (see Table 13-9). The costs considered, however, clearly do not account<br />

properly for the costs born by taxpayers and companies for the collection <strong>of</strong><br />

packaging, but only the funds which are required to be paid under the scheme being<br />

operated. Hence, they show the costs falling mostly upon the fillers/importers. This<br />

highlights, however, the difference between systems in the extent to which they are<br />

likely to lead to costs being passed onto the consumer through the price <strong>of</strong> products<br />

and services (rather than through taxation).<br />

29/09/09

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