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

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191<br />

• The effects <strong>of</strong> the Repak Payment System (RPS); 213 and<br />

• The landfill levy. 214<br />

Towards the end <strong>of</strong> 2000, a review <strong>of</strong> gate fees conducted by Kirk McClure Morton in<br />

the context <strong>of</strong> work establishing the basis for the landfill levy suggested that gate<br />

fees, in 1999, ranged from IR £15 (€19) per tonne to IR £32 (€41) per tonne for<br />

household and commercial and industrial waste, with one landfill charging a higher<br />

rate <strong>of</strong> IR £52 (€66) per tonne. By 2002, these had reached €102 per tonne, and by<br />

2005, €124.50 per tonne (pre landfill levy gate fees). In short, between 1999 and<br />

2005, the average costs <strong>of</strong> landfilling increased by a factor <strong>of</strong> 5 in nominal terms, or a<br />

factor <strong>of</strong> approximately 3.7 in real terms.<br />

In real 2005 terms, the differential was around €91 per tonne. Relative to the levy, at<br />

a maximum <strong>of</strong> €15 per tonne in these years, this is a huge change. Equally, for waste<br />

producers / collectors, because recycling ‘runs <strong>of</strong>f’ the avoided costs <strong>of</strong> disposal, this<br />

change will have had a significant impact.<br />

It would seem reasonable to suppose that for commercial waste in particular, with the<br />

relatively small (compared with those for household waste) levels <strong>of</strong> price support<br />

through the RPS supports outlined in Table 11-4 below, that the significant rise in<br />

landfill gate fees, as well as the (until recently) upward trend in materials prices would<br />

have been far more influential in increasing packaging waste recycling than the RPS<br />

rates themselves. These rates are only <strong>of</strong> any significance for steel and plastic.<br />

The rates for household waste are more likely to have been influential in determining<br />

the effort made to collect and recycle packaging waste (see Table 11-5). Yet the<br />

quantities <strong>of</strong> packaging recovered through the household stream are far lower than<br />

from the non-household stream (<strong>of</strong> the order a third <strong>of</strong> the recovered material.<br />

Table 11-4: RPS Rates for Commercial ‘Back Door’ <strong>Waste</strong> Recycled (2008 rates, € per<br />

tonne recycled)<br />

Material Material Open Open Loop Loop Closed Closed Loop Loop Recovery Recovery Metal Metal Protocol<br />

Protocol<br />

Glass 4.20 12.60<br />

Paper/Cardboard 4.20 9.45 4.20<br />

Wood 6.30 10.50 4.20<br />

Aluminium 10.50 12.50<br />

Steel 36.75 36.75 10.50<br />

Plastic 52.50 52.50<br />

Source: Repak<br />

213 See Appendix 12.0 for further information on the RPS.<br />

214 One could argue that the Environmental Fund should also be considered as a separate influence.<br />

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

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