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

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In an attempt to add a higher degree <strong>of</strong> resolution to the broad cost ranges shown in<br />

Table 25-4, the collection trials undertaken in the UK by WRAP can be examined. Due<br />

to the very nature <strong>of</strong> these trial schemes, coverage in many places was only a few<br />

thousand households, and thus, economies <strong>of</strong> scale were not achieved. WRAP was<br />

also keen to be able to monitor individual scheme performance to allow a thorough<br />

evaluation. This meant that a premium was paid for collection and reprocessing (the<br />

WRAP report suggests a cost reduction in the order <strong>of</strong> 40-50% would be possible if<br />

schemes were rolled out nationally). As for the tonnage performance already<br />

discussed the trial costs per tonne shown should not be viewed as indicative <strong>of</strong> a<br />

widespread national programme, but these costs are interesting from a relative<br />

perspective.<br />

Table 25-4: Cost Ranges for Existing Portable Battery Bring Back Collection Schemes<br />

472<br />

29/09/09<br />

Variable Variable Costs: Costs:<br />

Euros/tonne Euros/tonne <strong>of</strong> <strong>of</strong> portable portable batteries batteries collected<br />

collected<br />

Collection points (equipment) 50-150<br />

Collection (logistics) 250-550<br />

Sorting 150-250<br />

Transport and Recycling (excluding disposal) 400-900<br />

Fixed Fixed Fixed Costs:<br />

Costs:<br />

Public Relations and communication 50-1,700<br />

Administration 125-900<br />

TOTAL TOTAL<br />

1,115 1,115 – 3,765<br />

3,765<br />

Source: BIO Intelligence Service (2003), Impact Assessment on Selected <strong>Policy</strong> Options for Revision <strong>of</strong><br />

the Battery Directive, Final Report for EC, July 2003.<br />

http://ec.europa.eu/environment/waste/batteries/pdf/eia_batteries_final.pdf<br />

Table 25-5 shows that kerbside collections run by third sector organisations were the<br />

most expensive <strong>of</strong> the WRAP collection trial schemes and more than four times more<br />

expensive than municipal kerbside collection. WRAP suggest the reason for this<br />

significant difference is due to the terms <strong>of</strong> existing contracts with collection<br />

organisations that municipalities enjoy (i.e. some <strong>of</strong> these costs can be absorbed<br />

within the existing working day so that the new costs are marginal ones rather then<br />

being wholly additional).<br />

This explanation is supported by a kerbside recycling collection company in the UK<br />

(May Gurney) that collects portable batteries as part <strong>of</strong> its contracted services to<br />

municipalities. Due to the relatively small amounts <strong>of</strong> portable batteries collected, the<br />

net additional cost <strong>of</strong> collecting this material alongside a range <strong>of</strong> others is quite<br />

negligible, whilst reprocessing costs are <strong>of</strong>fset by the income the contractor receives<br />

from reprocessors for automotive batteries also collected from the kerbside. The<br />

extent <strong>of</strong> this cost <strong>of</strong>fsetting is, <strong>of</strong> course, dependant on the state <strong>of</strong> market.

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