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This is likely to have been dependent upon the weight based payments made by<br />

obligated entities, and the targets the scheme is required to meet. Some materials<br />

are lower in weight, but some <strong>of</strong> these, notably plastics, are more expensive to<br />

recycle.<br />

Reuse systems that had been based on glass (such as in Denmark and Finland) have<br />

been encouraged through tax policy to remain reuse rather than one-way, but start to<br />

move to PET bottles. This was the case after the Finnish tax was introduced in 1994,<br />

as shown in Table 13-8. Where legislative support has not been in place for reusable<br />

systems, these have tended to dramatically diminish.<br />

Table 13-8: Finnish Packaging Mix<br />

247<br />

1995 1995 Market Market Share Share %<br />

%<br />

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

1999 1999 Estimated Estimated<br />

Estimated<br />

Market Market Market Share Share % %<br />

%<br />

1995 1995-9 1995 9 Growth Growth Growth %<br />

%<br />

Cans 13 16 25<br />

Refillable Glass 77 64 -18<br />

Non-refillable Glass 0 0 0<br />

Refillable PET/PEN 9 19 97<br />

Non-refillable PET/PEN 0 0 0<br />

Total 100 100 -2<br />

Source: Study on Environmental Taxes and Charges in the EU, 2001<br />

There are a number <strong>of</strong> drivers for technical innovation in packaging and so it is not<br />

always simple to assign change to a particular one. For example, lightweighting <strong>of</strong><br />

aluminium cans would be driven by the price <strong>of</strong> the material, so the producer<br />

responsibility fee would have to be high in order to contribute more inducement.<br />

Some <strong>of</strong> the recent packaging changes do however point towards single material use,<br />

such as the all cardboard packaging for Duracell batteries or some small electrical<br />

appliances. In addition, the increase in use <strong>of</strong> re-usable packaging – particularly for<br />

haulage <strong>of</strong> products in crates / pallets has been incentivised by producer<br />

responsibility.<br />

13.8 Social and Distributional Consequences<br />

The cost <strong>of</strong> packaging waste collection and disposal is covered either by municipal<br />

charges or by a producer responsibility organisation. See Table 13-6 for the split in<br />

Europe. Where the majority <strong>of</strong> the cost is covered by the producer responsibility<br />

organisation, it is recouped via the producers from the cost <strong>of</strong> their products.<br />

Otherwise, it is charged directly to the householders either as a flat charge or a<br />

mixture <strong>of</strong> fixed and variable (by use) charges.<br />

13.9 Complementary Policies<br />

In a number <strong>of</strong> countries deposit refund systems are used in conjunction with<br />

producer responsibility. They are an attempt to increase recycling rates and address<br />

the problem <strong>of</strong> littering by giving an incentive to the consumer to take back the<br />

container. A one-way container tax is complementary to producer responsibility,

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