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sectoral economic costs and benefits of ghg mitigation - IPCC

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Transport<br />

for air pollution <strong>and</strong> noise. Impacts on habitants <strong>and</strong> communities might best be addressed<br />

through changes in transport system design. Nevertheless, fuel taxation is <strong>of</strong>ten discussed as a<br />

crude means <strong>of</strong> reflecting the externalities <strong>of</strong> road use to drivers for the same reasons (<strong>of</strong><br />

convenience) that governments frequently collect road funds through fuel taxes.<br />

This section examines the possible effects <strong>of</strong> externality adders in fuel taxes. This question was<br />

addressed in the three OECD case studies (Orfeuil, 1995; Morisugi, 1995; DRI, 1996). For<br />

externality adders evaluation the country case studies use a variety <strong>of</strong> carbon emission <strong>costs</strong> as<br />

shown in Table 2.<br />

Table 2<br />

Social Costs Associated with CO 2 emissions<br />

FRANCE JAPAN UNITED STATES<br />

$ per tonne <strong>of</strong> CO 2 5.5 to 19 20(a) 3.2 to 13<br />

Total CO 2 external cost (billion $) 0.6 to 2.5 4 1.8 to 8.6<br />

CO 2 external cost/vehicle-km ($) 0.0015 to 0.006 0.006 0.0008 to 0.003<br />

CO 2 external cost / GDP 0.05% to 0.21% 0.12% 0.03% to 0.15%<br />

(a) secretariat estimate<br />

Source: Michaelis, 1996<br />

Other externality estimates are also available from the same case studies including road<br />

accidents, noise, local air pollution, <strong>and</strong> congestion. Overall externality estimates for road<br />

transport are: US$ 16-24 billion in France in 1991, rising to $18-29 billion in 2010; US$ 21<br />

billion in Japan in 1991, rising to $24 billion in 2010; <strong>and</strong> in excess <strong>of</strong> US$ 118-371 billion in the<br />

United States in 1991. However, these estimates are not evaluated on a comparable basis; any<br />

common action including the use <strong>of</strong> externality adders would probably depend on developing<br />

comparable externality estimates.<br />

Based on studies, using externality adders in fuel taxes would imply the fuel price increases as<br />

shown below in Table 3, where <strong>costs</strong> <strong>of</strong> road provision have also been included. Again, it must<br />

be emphasized that these prices are used for illustration purposes only. Countries considering<br />

raising fuel taxes to reflect the full social <strong>costs</strong> <strong>of</strong> transport would need to carry out their own<br />

detailed analysis <strong>of</strong> those <strong>costs</strong>, <strong>and</strong> <strong>of</strong> the best way to address them.<br />

Table 3<br />

Fuel Price Changes for Full Social Cost Pricing<br />

REGION<br />

Sample country<br />

where subsidies<br />

were estimated<br />

North<br />

America<br />

OECD<br />

Europe<br />

OECD Pacific<br />

Central/<br />

Eastern<br />

Europe<br />

United States France* Japan* Not Estimated Russia fuel<br />

subsidies only<br />

(as previous<br />

section)<br />

Base Full Base Full Base Full Base Full Base Full Cost<br />

Cost<br />

Cost<br />

Cost<br />

Cost<br />

Gasoline 29 53-106 85 103-121 115 148 50 NE 30 30<br />

Diesel 29 53-106 60 103-121 76 148 40 NE 7.5 15<br />

* Externalities estimated in these countries are used for illustrative purposes in modeling transport energy<br />

use in the regions, although the countries are not necessarily representative <strong>of</strong> others in their regions.<br />

Source: Michaelis, 1996<br />

CIS<br />

194

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