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

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Note 2: For the first two biodegradable waste diversion obligations (2010 & 2013), a<br />

national 3 bin system (including for catering/ commercial sources <strong>of</strong><br />

biowastes) will likely ensure, on its own, that the EU Landfill Directive<br />

diversion/treatment obligations are met through diversion from landfill <strong>of</strong> the<br />

biodegradable dry recyclables and the organics.<br />

Note 3: This will translate (approximately) to the tonnage <strong>of</strong> BMW accepted at<br />

landfills in 2010 being less than 25% <strong>of</strong> the tonnage MSW generated<br />

nationally; falling to < 15% in 2013, and < 9% in 2016.<br />

Note 4: SRF – Solid Recovered Fuel <strong>of</strong> defined specification for use as a fuel in coincineration<br />

plants, or other energy uses as may be approved, where<br />

available.<br />

Source: EPA (2009) Municipal Solid <strong>Waste</strong> - Pre-treatment and Residuals<br />

<strong>Management</strong>: An EPA Technical Guidance Document, Johnstown Castle Estate: EPA.<br />

In the medium- term, the establishment <strong>of</strong> a stability threshold is to be welcome.<br />

However, the Guidance document does not spell out unequivocally that the meeting<br />

<strong>of</strong> the stability criterion is intended to imply that the waste will be treated as ‘no<br />

longer biodegradable’ for the purposes <strong>of</strong> the Landfill Directive. Indeed, if such a<br />

measure had been considered earlier, this would have been the only measure<br />

required to implement the Landfill Directive, though other instruments would have<br />

been necessary to ensure that environmental benefits were realised through the<br />

approach. 881 In practice, it might be preferable for the Guidance to:<br />

718<br />

� Establish a pre-treatment requirement independently <strong>of</strong> the meeting <strong>of</strong> Landfill<br />

Directive targets, this being specified to allow the requirements to be easily<br />

met. 882 There does not, after all, appear to be any underpinning rationale for<br />

suggesting that what constitutes pre-treatment one day is not pre-treatment<br />

on another, but the Guidance appears to change the requirement for ‘pretreatment’<br />

in line with what is required to deliver Landfill Directive targets. This<br />

would allow the Government to discharge its obligations under Article 6 <strong>of</strong> the<br />

Landfill Directive; and<br />

� Establish a stability threshold for landfilling <strong>of</strong> all municipal waste, this<br />

requirement to be met not by 2016, but by 2013. Where, in a given region, the<br />

necessary infrastructure is absent, exemptions would be granted, but only<br />

where applied for in advance, and at additional cost to the holder <strong>of</strong> the waste.<br />

881 This measure alone would not necessarily have delivered the most desirable outcome. It might,<br />

however, have delivered on the Directive targets since it would have implied that no biodegradable<br />

municipal waste could be landfilled.<br />

882 The UK provides one example <strong>of</strong> a country which has defined pre-treatment very loosely. Pretreatment<br />

includes most activities which alter the nature <strong>of</strong> the waste, including sorting <strong>of</strong> a material<br />

from the waste stream. There are definitely drawbacks in such an approach, but the urgency <strong>of</strong><br />

meeting the Article 6 targets might suggest a similarly simple approach. In Scotland, the regulator<br />

effectively assumes that the pre-treatment requirements are met so that the measure implies very little<br />

for waste producers (though some collectors have used the requirements to encourage some<br />

customers to sort materials where they had not been doing so previously).<br />

29/09/09

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