sectoral economic costs and benefits of ghg mitigation - IPCC
sectoral economic costs and benefits of ghg mitigation - IPCC
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