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private sector operators incur costs when unplanned changes to services are<br />

introduced and so even where the actors involved are willing participants in the<br />

change, there may be reluctance to make the switch quite as quickly as might be<br />

desired. Finally, we note that there appears to be no sanction proposed for<br />

application to those City and County Managers who do not follow the Circular’s<br />

recommendations, let alone to those private sector operators who might be reluctant<br />

to change their collection service before they have to.<br />

33.7 Environmental Benefits<br />

The aim <strong>of</strong> the Circular is to ensure that biodegradable waste which might otherwise<br />

be landfilled is dealt with through alternative means. In environmental terms, reports<br />

elsewhere suggest that the net benefits <strong>of</strong> such an approach will depend considerably<br />

on: 623<br />

535<br />

� The design <strong>of</strong> the collection system;<br />

� The choice <strong>of</strong> treatment system for collected biowaste; and<br />

� The charging system applied in the context <strong>of</strong> the collection system used.<br />

The reason environmental benefits may not be secured by the policy relate to the way<br />

in which the two principal fractions <strong>of</strong> the targeted organic waste – food waste and<br />

garden waste – behave when they are targeted for collection. Studies in the UK and<br />

elsewhere highlight the potential for considerable quantities <strong>of</strong> garden waste to be<br />

collected where garden waste services are <strong>of</strong>fered free <strong>of</strong> charge. One report refers to<br />

this as the problem <strong>of</strong> a ‘latent garden waste fraction’, lending itself to the possibility<br />

that collected organic waste increases significantly in tonnage terms.<br />

Data in Figure 33-1 shows two years <strong>of</strong> total waste arisings tonnage data for a UK<br />

authority where a free garden waste collection service was put in place. In our<br />

experience, this is a typical outcome in temperate countries such as the UK and<br />

Ireland. The difference between the two lines <strong>of</strong> data represents the quantity <strong>of</strong><br />

garden waste that was separately collected. The service was trialled for a limited<br />

number <strong>of</strong> households in the first year before being provided to all households in the<br />

second year. Several important characteristics <strong>of</strong> garden waste generation and the<br />

impacts <strong>of</strong> collection services can be observed in the data:<br />

• Firstly, the impact <strong>of</strong> providing a new and free collection service is seen to<br />

increase total waste arisings; this can largely be attributed to a reduction in<br />

home composting and a potential encouragement <strong>of</strong> harvesting a latent<br />

garden waste fraction (i.e. the new outlet for garden waste brings<br />

additional material into the waste management system that was either not<br />

created or previously managed at source – material from hedge cutting for<br />

instance);<br />

623 Eunomia (2007) Managing Biowastes from Households in the UK: Applying Life-cycle Thinking in<br />

the Framework <strong>of</strong> Cost-benefit Analysis, Banbury, Oxon: WRAP.<br />

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

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