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

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40<br />

29/09/09<br />

system. Another is Carpet America Recovery Effort (CARE), created by an<br />

agreement that arose from a 2002 MOU between manufacturers, several<br />

state governments and the US EPA. The memorandum set voluntary recycling<br />

rate goals for carpet to be reached by 2012;<br />

� Advance recycling fees – An ARF – which was originally referred to as an<br />

advance disposal fee, or ADF – is a tax assessed on product sales and <strong>of</strong>ten<br />

used to cover the cost <strong>of</strong> recycling. ARFs are <strong>of</strong>ten assessed per unit <strong>of</strong> the<br />

product sold but can also be assessed on the basis <strong>of</strong> weight. ARFs may be<br />

visible to the consumer on the purchase <strong>of</strong> a product, as a separate line on the<br />

bill, or imposed upstream on producers and later incorporated in the sales<br />

price; and<br />

� ARF combined with a recycling subsidy – An ARF raises money that can be<br />

used in a variety <strong>of</strong> ways. The incentive effects <strong>of</strong> the policy depend greatly on<br />

both the type <strong>of</strong> ARF and the use <strong>of</strong> revenues. A ‘back-end’ recycling subsidy –<br />

either a subsidy per unit <strong>of</strong> the product recycled or unit weight <strong>of</strong> material<br />

recycled – leads to quite a different policy instrument than one in which ARF<br />

revenues are used to cover waste management cost or infrastructure costs in<br />

a lump-sum fashion. California’s used oil programme, the western Canada<br />

used oil programme, lead-acid batter programmes in several US states, and<br />

California’s e-waste programme are all ARF/recycling subsidy programs.<br />

All <strong>of</strong> these policy instruments make the producer financially or physically responsible<br />

for the end-<strong>of</strong>-life environmental impacts <strong>of</strong> his product. In this sense, they could all<br />

be considered EPR. However, they have very different incentive effects and ultimately<br />

may lead to different environmental outcomes, and the costs <strong>of</strong> the instrument may<br />

differ widely.<br />

Other non-EPR policy instruments can lead to similar outcomes but do not focus<br />

upstream on producers. To illustrate the contrast, four such non-EPR instruments are<br />

outlined below<br />

� Landfill bans – Many US states and European countries ban disposal <strong>of</strong><br />

particular items in landfills (or incinerators);<br />

� ‘Pay as you throw’ pricing <strong>of</strong> waste collection/disposal – A large number <strong>of</strong><br />

Irish authorities, as well as many municipalities in the EU, more than 4,000<br />

communities in the US, all municipalities in South Korea and many other<br />

municipalities in other countries besides, charge for the collection and<br />

management <strong>of</strong> waste using a variable fee element. In some countries, end-<strong>of</strong>life<br />

fees are charged for specific items that are difficult to dispose <strong>of</strong>. None <strong>of</strong><br />

these policies are aimed at the producer, and so do not qualify as EPR, but<br />

they do have some effects on waste generation and recycling, usually through<br />

affecting consumption decisions and through changing citizens’ behaviour.<br />

� Recycling subsidies – The government may raise funds in ways that are not<br />

ARFs/ADFs, and subsidize recycling. The government could make a payment<br />

per unit or kg <strong>of</strong> material recycled, or it could make lump-sum grants to<br />

communities or recycling centres. Such grants are quite common in the US.<br />

Whether the subsidy is per unit volume, per unit <strong>of</strong> weight, or a one time lump<br />

sum will have different effects; and

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