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

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51.4 Existing Targets<br />

Several targets apply to Ireland through the application <strong>of</strong> EU legislation, whilst others<br />

have been set at the national level in support <strong>of</strong> the delivery <strong>of</strong> EU targets. A brief<br />

review <strong>of</strong> these is <strong>of</strong>fered below.<br />

51.4.1 Landfill Directive<br />

In 1995, Ireland landfilled 1.29 million tonnes <strong>of</strong> biodegradable municipal waste<br />

(BMW). 865 The Landfill Directive targets imply, therefore, that:<br />

706<br />

• No more than 967 thousand tonnes <strong>of</strong> biodegradable municipal waste may be<br />

landfilled in 2010;<br />

• No more than 645 thousand tonnes <strong>of</strong> biodegradable municipal waste may be<br />

landfilled in 2013; and<br />

• No more than 451 thousand tonnes <strong>of</strong> biodegradable municipal waste may be<br />

landfilled in 2016.<br />

The targets imply successive reductions in absolute quantities <strong>of</strong> BMW being<br />

landfilled. For Ireland, the most worrying fact is that despite improvements in<br />

recycling <strong>of</strong> household and commercial waste, the rate <strong>of</strong> growth in BMW has nullified<br />

these efforts in terms <strong>of</strong> their contribution to Landfill Directive targets. The country<br />

appears to be ‘running to stand still’, with landfilled BMW still higher in 2007 than it<br />

was in 1995 (see Figure 51-5).<br />

This re-iterates the points made earlier concerning:<br />

� the need to be clear about whether what is classified as commercial waste<br />

really is commercial waste. The growth in what is reported as BMW, and the<br />

actual quantity <strong>of</strong> BMW may be two completely different things. 866 Given the<br />

potential ramifications (in terms <strong>of</strong> cost and timing) <strong>of</strong> over-estimating MSW,<br />

and hence (through applying composition data derived from Characterisation<br />

Studies related to specific waste streams), BMW, some detailed investigations,<br />

and potentially, even measures to keep waste streams separate, might be<br />

desirable; and<br />

� the need to step up activity in respect <strong>of</strong> source separation <strong>of</strong> the major<br />

components <strong>of</strong> biowaste.<br />

elaborated. The EPA is clearly – on the basis <strong>of</strong> communications with them - confident that the<br />

Guidance will achieve what it sets out to. However, confidence in this regard might have been<br />

enhanced had the document been clearer on a number <strong>of</strong> matters which are <strong>of</strong> material significance.<br />

865 EPA (2003) National <strong>Waste</strong> Report 2001, Johnstown Castle Estate: EPA.<br />

866 The EPA recognises that the basis for understanding the composition <strong>of</strong> BMW in the waste stream<br />

is not ideal from the perspective <strong>of</strong> what is reported as municipal waste by landfill operators. According<br />

to personal communications, the supposition is that ‘genuine’ municipal waste is frequently mixed with<br />

other materials, such as C&D waste, before being sent to landfill, where all the material is declared as<br />

MSW.<br />

29/09/09

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