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

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Table 8-10: Summarised Cost Benefit <strong>of</strong> the Introduction <strong>of</strong> Charging Schemes in<br />

England<br />

Additional Costs due to rerouting <strong>of</strong> Garden and Bulky <strong>Waste</strong> to CA Sites<br />

Change Change<br />

Change<br />

(£/hhld)<br />

(£/hhld)<br />

£0.38<br />

Introduction Costs £2.82<br />

Billing Costs £4.83<br />

Fly-tip Costs £1.73<br />

Change in Kerbside Collection and Treatment / Disposal Costs -£13.95<br />

Net Costs -£4.19<br />

Source: Hogg, D., Wilson, D., Gibbs, A., Astley, M., Papineschi, J. (2006) Modelling the Impact <strong>of</strong><br />

Household Charging for <strong>Waste</strong> in England, Final Report to Defra.<br />

Annual costs <strong>of</strong> organising and administering billing were modelled at £4.83 per<br />

household. As noted above, it is questionable whether this cost is genuinely<br />

‘additional’ in the Irish context.<br />

It should be noted that these costs were modelling costs (based on researched<br />

itemised costs) for partial (71%) roll out <strong>of</strong> a range <strong>of</strong> different charging schemes<br />

across England. What is not shown in the headline table is the cost benefit <strong>of</strong><br />

universal roll out <strong>of</strong> one or other particular charging approach in any particular local<br />

authority. Sensitivity analysis revealed that the net cost/benefit per charged<br />

household if preferential (the most effective and efficient) charging schemes were<br />

employed may result in an annual saving <strong>of</strong> almost £12 per household. Greenhouse<br />

gas savings are additional to this figure, and as shown in Section 8.5.10 may be in<br />

excess <strong>of</strong> £3 per household depending upon one’s assumptions, and the nature <strong>of</strong><br />

the systems used.<br />

The true delivery <strong>of</strong> these cost savings inherently necessitates a strong and freeflowing<br />

financial relationship between the bodies responsible for waste management<br />

and administration at every level. In practice, policies needs to be carefully<br />

constructed if this is to happen (i.e. to ensure that collection cost savings and avoided<br />

disposal savings contribute to the clean up <strong>of</strong> fly-tips etc.).<br />

8.7 Effects on Technical Change / Innovation<br />

In terms <strong>of</strong> waste prevention, the nature <strong>of</strong> changes tends to be related to purchasing<br />

decisions, and increasing home composting. There is some anecdotal evidence which<br />

suggests that where pay-by-use systems are in place, householders tend demand<br />

reduced packaging. A report for SNIFFER undertook surveys <strong>of</strong> multinational<br />

companies, some <strong>of</strong> whom hinted at possible effects <strong>of</strong> charging on packaging<br />

design: 183<br />

183 Eunomia Research & Consulting and M. E. L. Research for ECOTEC Research & Consulting (2002)<br />

Towards Sustainable <strong>Waste</strong> <strong>Management</strong> Practice, Report for SNIFFER, SR(02)05a, April 2002.<br />

148<br />

29/09/09

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