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

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specific battery types, they might exceed the estimate made here (which, in any case,<br />

majors on greenhouse gas and air pollution consequences – some <strong>of</strong> the effects are<br />

likely to be in reduced hazards <strong>of</strong> disposal which are more difficult to capture in a<br />

basic analysis).<br />

The next section highlights some analyses which look at the general environmental<br />

benefits <strong>of</strong> the removal <strong>of</strong> hazardous substances and increased recycling. Taking the<br />

performance in terms <strong>of</strong> collection and recycling as a proxy for environmental<br />

performance, we then review the factors which seem influential in driving<br />

improvements in collection rates.<br />

25.5.2 Environmental Consequences <strong>of</strong> Producer Responsibility for<br />

Batteries<br />

Several <strong>of</strong> the reports mentioned in previous sections have commented on the<br />

environmental benefits <strong>of</strong> battery collections.<br />

The Impact Assessment on Selected <strong>Policy</strong> Options for Revision <strong>of</strong> the Battery<br />

Directive states the relatively obvious – that the establishment <strong>of</strong> separate collection<br />

targets are expected to have positive consequences in terms <strong>of</strong> controls on the<br />

hazardous substances contained within batteries and also in the use <strong>of</strong> recycled<br />

rather than virgin materials (though these positive benefits may be partially <strong>of</strong>fset by<br />

the environmental impacts due to additional activities required to separate, collect<br />

and recycle batteries). 550 It should be noted however that transport logistics are not,<br />

usually, a decisive factor in determining impacts in environmental terms, especially,<br />

as here, when the external benefits <strong>of</strong> recycling are potentially so high.<br />

While a lack <strong>of</strong> LCA data meant that it was not possible to assess the overall<br />

environmental balance <strong>of</strong> collecting and recycling all portable batteries, an<br />

assessment <strong>of</strong> NiCd batteries showed that there would be environmental benefits 2.5<br />

to 13 times higher than the baseline scenario. Whilst this is a wide range, since<br />

cadmium batteries are classified as hazardous waste and its substitutes (Nickel-<br />

Metal Hydride and Lithium chemistries) are not, one can conclude that the phasing<br />

out <strong>of</strong> cadmium batteries would result in decreased environmental impacts in the<br />

future.<br />

The same study estimates the amount <strong>of</strong> metals which could be recovered from<br />

portable batteries annually across the EU at 66,028 tonnes, the breakdown <strong>of</strong> which<br />

is shown in Table 19-2. It should be noted that these figures are based on portable<br />

battery sales information from 2002 and as such the levels <strong>of</strong> the hazardous<br />

substance cadmium are relatively high. With the tight restrictions on the use <strong>of</strong><br />

cadmium put forward in the Directive, and the banning <strong>of</strong> NiCd batteries in all but a<br />

few applications, there has been a significant reduction in the amount <strong>of</strong> cadmium<br />

being used in portable battery production for the EU market in recent years. For<br />

example, in Germany, from 2003 to 2007, the quantity in tonnage terms <strong>of</strong> NiCd<br />

550 BIO Intelligence Service (2003).<br />

467<br />

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

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