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

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716<br />

4. Effectively push for source separation <strong>of</strong> dry recyclables and biodegradable<br />

wastes.<br />

Particularly in respect <strong>of</strong> the last <strong>of</strong> these four points, it is not clear that the approach<br />

is the best mechanism. However, a reader <strong>of</strong> the document could be forgiven for<br />

thinking that the Guidance is effectively seeking to become ‘the measure’ by which<br />

Ireland meets its Landfill Directive targets in a fairly encompassing approach.<br />

In general, the Guidance is well intended. However, some issues remain outstanding<br />

on a reading <strong>of</strong> the document, including:<br />

� It lacks a detailed description <strong>of</strong> exactly what is expected to happen when the<br />

Guidance enters into force (as, in principle, it already has done). The date<br />

appears to have been set more with regard to the date set for complying with<br />

Article 6;<br />

� It stipulates some requirements which may deliver rather marginal benefit<br />

whilst imposing significant costs. Notable in this regard is the shift from a<br />

stability standard <strong>of</strong> 10 mg O2/g d.m. down to 7 mg O2/g d.m. The rationale<br />

given is that the approach is in line with continuous improvement outlined<br />

under BAT, but this does open up a range <strong>of</strong> questions regarding, for example,<br />

whether benefits are commensurate with costs, and how the same approach<br />

is translated to other facilities to which the requirement to demonstrate BAT<br />

also applies; 880<br />

� The targets for operators are set in terms <strong>of</strong> the proportion <strong>of</strong> BMW in MSW<br />

accepted at landfills, which might be an awkward way to specify the means to<br />

meet Landfill Directive targets unless the management <strong>of</strong> Irish waste in future<br />

follows the exact path which seems to have been modelled for it; and<br />

� It would seem to be incredibly difficult (perhaps impossible) to enforce the<br />

targets in a meaningful way, especially in the short term, and it is notable that<br />

no discussion on the issue <strong>of</strong> regulation and enforcement is to be found within<br />

the document.<br />

Notwithstanding the above comments, the EPA remains confident in its approach,<br />

and that the outcome will be satisfactory, but it is clear that the approach is very<br />

much in the development phase.<br />

880 In communications, the EPA expresses the view that this delivers additional reductions in<br />

biodegradability, which is no doubt true. The problem is that in order to meet the revised target, in<br />

principle, no change in ‘technique’ is necessarily required. Rather, the change is likely to lead to a<br />

considerable increase in the cost <strong>of</strong> achieving the standard through increasing the necessary retention<br />

time (although, no doubt, additional re-jigging <strong>of</strong> the facility could be made to achieve the higher<br />

standard, but mid-operation, this would be expensive). The extent to which this benefit could be said to<br />

be worth the additional cost <strong>of</strong> meeting the amended standard is not clear, but our own research<br />

suggests that the opposite is likely to be the case, possibly with a substantial cost for minimal benefit<br />

(see, for example, Eunomia (2008) ‘Biostabilisation’ <strong>of</strong> wastes: making the Case for a Differential Rate<br />

<strong>of</strong> Landfill Tax,<br />

http://www.eunomia.co.uk/shopimages/Eunomia%20Landfill%20Tax%20Paper%20Final.pdf )<br />

29/09/09

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