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

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Transport externalities were incorporated into the assessment <strong>of</strong> externalities<br />

(through use <strong>of</strong> typical distances). It is somewhat debatable whether consideration <strong>of</strong><br />

externalities related to waste management facilities should consider transport<br />

externalities as part <strong>of</strong> the ‘process related’ externality (implying that, in some way, a<br />

particular facility always has associated with it a more or less well understood<br />

transport externality). To the extent that transport externalities can be altered through<br />

changed transportation modes as well as distances, such an analysis appears to<br />

obscure the possibilities for improvement, or indeed, for their being addressed by<br />

transport policies. Indeed, a number <strong>of</strong> instruments, notably, in the UK, the fuel duty<br />

escalator, have been introduced since the CSERGE work was undertaken. These<br />

effectively internalise transport related externalities to some extent. Consequently,<br />

their inclusion in ‘process-specific’ estimates <strong>of</strong> externalities is somewhat<br />

problematic. Several authors have opined that the UK fuel duty escalator internalises<br />

either completely, or to a significant degree, the external costs. This is an issue which<br />

we return to later. It is worth pointing out that since 1993, emissions <strong>of</strong> some <strong>of</strong> the<br />

key pollutants on a per tonne per kilometre basis, notably NOx, have diminished<br />

significantly.<br />

The study made no attempt to consider the fact that emissions from landfill occur<br />

over an extended period <strong>of</strong> time. Methane is not emitted from landfills<br />

instantaneously, whereas the greenhouse gases from incinerators are. It would seem<br />

to be appropriate to apply a discount factor (or at least, to justify not applying one)<br />

where landfills are concerned. If it is deemed to be important to consider a non-zero<br />

discount rate, then making a simple distinction between biogenic and non-biogenic<br />

carbon, and assuming carbon dioxide from non-biogenic carbon is unimportant,<br />

cannot be justified. This is because the emissions <strong>of</strong> biogenic carbon dioxide occur at<br />

different rates from landfills and incinerators (and waste management facilities more<br />

generally). 1165<br />

61.3.2 HM Customs & Excise<br />

Just as the CSERGE et al study was used to inform the discussions concerning a<br />

landfill tax, so the work which culminated in the paper by HM Customs & Excise was<br />

important in informing the debate concerning an incineration tax. 1166 The final output<br />

– the HM Customs & Excise Report – is interesting for a number <strong>of</strong> reasons. These<br />

are discussed below.<br />

1165 D. Hogg et al (2002) Economic Assessment <strong>of</strong> Options for Dealing with Biodegradable <strong>Waste</strong>,<br />

Report to DG Environment, European Commission, by Eunomia, Scuola Agraria del Parco di Monza,<br />

HDRA Consultants, ZREU and LDK.<br />

1166 Enviros, University <strong>of</strong> Birmingham, RPA Ltd., Open University and Maggie Thurgood (2004) <strong>Review</strong><br />

<strong>of</strong> Environmental and Health Effects <strong>of</strong> <strong>Waste</strong> <strong>Management</strong>: Municipal Solid <strong>Waste</strong> and Similar<br />

<strong>Waste</strong>s, Final Report to Defra, March 2004); Enviros and EFTEC (2004) Valuation Of The External<br />

Costs And Benefits To Health And Environment Of <strong>Waste</strong> <strong>Management</strong> Options Final Report for Defra,<br />

December 2004.<br />

949<br />

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

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