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

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829<br />

figures include nappies, as is the case in Ireland, but our experience suggests<br />

they would not. The general picture, however, is that there is very significant<br />

potential for progress to be made in this area in Ireland, and that through<br />

capturing around 50% <strong>of</strong> the non-nappy textiles, an additional 40,000 tonnes<br />

or so <strong>of</strong> landfilled waste could be avoided; 1041<br />

In the following scenario we have assumed that:<br />

� Growth rates are as previously projected;<br />

� The capture rate for paper and card increases to 60%;<br />

� Textiles recycling / re-use rates increase to 15% <strong>of</strong> total (around 30% <strong>of</strong> nonnappy<br />

textiles), in line with the National Biodegradable <strong>Waste</strong> Strategy; and<br />

� Organic waste captures increase to 30% in 2010.<br />

Other material captures are increased slightly from the previous scenario (reflecting,<br />

as with paper and card, increased efforts to sort). The results from this scenario are<br />

shown in Figure 56-2. The Scenario would require capacity for treatment <strong>of</strong> source<br />

segregated organics to be <strong>of</strong> the order 250,000 tonnes, an increase <strong>of</strong> 170,000<br />

tonnes or so from 2007.<br />

A critical variable will be the change in gross quantities <strong>of</strong> MSW, and in particular, the<br />

effect that the recession has had upon this. Even so, they highlight the fact that even<br />

with these efforts, there would be 143,170 tonnes more BMW in residual waste than<br />

could be landfilled. This is equivalent to the BMW contained in 208,000 tonnes <strong>of</strong><br />

residual MSW.<br />

The treatment possibilities for this residual waste then become important. Here, there<br />

appear to be four possibilities:<br />

1. The residual waste is incinerated. There would appear to be only one<br />

possibility in this respect by 2010. This is the Carranstown plant at Meath,<br />

though it seems unlikely that this would be operating for the whole year, even<br />

if it was operating for part there<strong>of</strong> (and it might not be);<br />

2. The residual waste is used in the preparation <strong>of</strong> SRF for export. This has been<br />

happening for some years, with more that 30,000 tonnes exported to UK and<br />

Sweden in 2007;<br />

1041 It is far from clear to us why ‘textiles’ should be treated as 100% biodegradable for the purposes <strong>of</strong><br />

the Landfill Directive. There are many synthetic textiles available and the fact that Ireland’s<br />

performance in respect <strong>of</strong> capturing textiles is relatively poor simply increases the magnitude <strong>of</strong> the<br />

task ahead. Effectively, the approach overstates the quantity <strong>of</strong> biodegradable waste in the waste<br />

stream, making it more difficult to meet a target in any given year. According to a recent life-cycle study<br />

on nappies, 16.8% <strong>of</strong> the weight <strong>of</strong> nappies disposed is not biodegradable (ERM (2008) An Updated<br />

Lifecycle Assessment Study for Disposable and Reusable Nappies, Report for WRAP and Defra,<br />

Science Report SC010018/SR2, October 2008). In the UK, it is generally assumed that 50% by weight<br />

<strong>of</strong> textiles are biodegradable, and whilst this may not be strictly accurate, it implies a pragmatic<br />

approach to the issue that not all textiles are biodegradable. This matter is taken up below.<br />

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

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