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

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ecycling to meet its targets (such as in the UK) then the cheapest sources will be<br />

addressed first. As recycling targets are increased then the cheaper – commercial<br />

and industrial sectors – will have to be supplemented by household recycling, and the<br />

higher cost <strong>of</strong> collection will increase the overall cost (which will then be passed onto<br />

the consumer).<br />

One report that examined the cost effectiveness <strong>of</strong> packaging recycling concluded<br />

that amongst France, Germany, the Netherlands and the UK, Germany accrued the<br />

greatest environmental benefits and recycling rates but at a higher cost per unit. 264<br />

This is likely to be inevitable as the recycling performance improves as this<br />

necessarily implies having to collect packaging from higher cost sources. It does not<br />

necessarily imply that such collections should not be undertaken.<br />

Indeed, the above analysis suggests that, not only in terms <strong>of</strong> principles, but also,<br />

potentially in respect <strong>of</strong> performance, schemes which require producers to fund 100%<br />

<strong>of</strong> the costs <strong>of</strong> collection <strong>of</strong> household packaging, and which require services to be<br />

provided to all householders, are likely to deliver highest performance. Without strong<br />

coverage <strong>of</strong> households, rate <strong>of</strong> recycling far in excess <strong>of</strong> 60% or so are likely to be<br />

more difficult to achieve. The top 3 performing countries – Austria, Germany and<br />

Belgium – also all make widespread use <strong>of</strong> PBU schemes at the household level.<br />

Another message is that recycling <strong>of</strong> packaging does, where logistics are efficient,<br />

deliver environmental benefits. These have been well documented in respect <strong>of</strong> GHG<br />

emissions, though our analysis suggests they apply equally in terms <strong>of</strong> non-GHG air<br />

pollutants (see Annex 63.0).<br />

Key recommendations from the Packflow 2008 report for the UK were as follows: 265<br />

i) Non Non-compliance Non compliance penalties penalties. penalties<br />

The packaging regulations should be amended at the<br />

earliest opportunity to introduce a mechanism for dealing with non-compliance by<br />

imposing non-criminal tonnage-related financial penalty charges on compliance<br />

schemes and producers that fail to meet their obligations. The revenue from these<br />

charges should be used to enhance UK packaging recycling and recovery.<br />

ii) Targets Targets. Targets . Business Targets for the years 2006 to 2008 should be calculated from<br />

the estimates in the likely growth <strong>of</strong> obligated tonnage. In addition the Government<br />

should adopt a process, ideally not requiring continual amendment <strong>of</strong> regulations, to<br />

set 5-year rolling targets extending beyond 2008 and allowing targets to be managed<br />

through regular annual review.<br />

iii) Packaging Packaging obligation obligation and and recovery recovery data data. data There is a need for more accurate and<br />

timely data and it is essential if sound target setting and review is to be<br />

accomplished.<br />

264 Taylor Nelson S<strong>of</strong>res, 2000 Cost-Efficiency Of Packaging Recovery Systems- the Case Of France,<br />

Germany, The Netherlands And The United Kingdom, Report for the European Commission, Feb 2000.<br />

265 Adapted from the Packflow 2008 report,<br />

http://www.valpak.co.uk/docs/packaging/packflow_2008_summary_report_recommendations.pdf<br />

250<br />

29/09/09

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