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Energy Subsidies: Lessons Learned in Assessing their Impact - UNEP

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<strong>Energy</strong> <strong>Subsidies</strong>: <strong>Lessons</strong> <strong>Learned</strong> <strong>in</strong> Assess<strong>in</strong>g <strong>their</strong> <strong>Impact</strong> and Design<strong>in</strong>g Policy Reforms<br />

Table A5: Unit Damage Costs of Air Pollutants from the ExternE Project (1995 €/tonne)<br />

Country<br />

SO2<br />

NOx<br />

Particulates<br />

Austria<br />

9,000<br />

16,800<br />

16,800<br />

Belgium<br />

11,388-12,141<br />

11,526-12,296<br />

24,536-24,537<br />

Denmark<br />

2,990-4,216<br />

3,280-4,728<br />

3,390-6,666<br />

F<strong>in</strong>land<br />

1,027-1,486<br />

852-1,388<br />

1,340-2,611<br />

France<br />

7,500-15,300<br />

10,800-18,000<br />

6,100-57,000<br />

Germany<br />

1,800-13,688<br />

10,945-15,100<br />

19,500-23,415<br />

Greece<br />

1,978-7,832<br />

1,240-7,798<br />

2,014-8,278<br />

Ireland<br />

2,800-5,300<br />

2,750-3,000<br />

2,800-5,415<br />

Italy<br />

5,700-12,000<br />

4,600-13,567<br />

5,700-20,700<br />

Netherlands<br />

6,205-7,581<br />

5,480-6,085<br />

15,006-16,830<br />

Portugal<br />

4,960-5,242<br />

5,975-6,562<br />

5,565-6,955<br />

Spa<strong>in</strong><br />

4,219-9,583<br />

4,651-12,056<br />

4,418-20,250<br />

Sweden<br />

2,357-2,810<br />

1,957-2,340<br />

2,732-3,840<br />

United K<strong>in</strong>gdom<br />

6,027-10,025<br />

5,736-9,612<br />

8,000-22,917<br />

Source: De Nocker, Saez and L<strong>in</strong>ares (1999).<br />

Some recent studies have exam<strong>in</strong>ed the local benefits associated with a reduction <strong>in</strong> air<br />

pollution brought about as a result of action to meet a target for reduc<strong>in</strong>g climate-destabilis<strong>in</strong>g<br />

greenhouse gas emissions. A 2000 study on Ch<strong>in</strong>a by Garbaccio and Jorgensen estimated that<br />

reductions <strong>in</strong> carbon emissions of 5% per annum, compared with a base case, would cut<br />

premature deaths by around 4% and reduce hospital visits and days lost from sickness. Us<strong>in</strong>g<br />

standard valuation methods, these benefits were converted <strong>in</strong>to a ga<strong>in</strong> <strong>in</strong> gross domestic<br />

product of 0.2% per year, equivalent to about $2 billion <strong>in</strong> 2000. A 1995 study by Larsen and<br />

Shah estimates that remov<strong>in</strong>g subsidies to energy production <strong>in</strong> Ch<strong>in</strong>a would reduce carbon<br />

emissions by about 7%. Therefore, energy-subsidy removal would be expected to yield an<br />

environmental health benefit of around 0.3% of GDP. The results for Ch<strong>in</strong>a can be applied to<br />

the world as a whole to give a rough figure on the potential local environmental ga<strong>in</strong> from<br />

energy-subsidy removal. Larsen and Shah estimated that global subsidy removal would<br />

reduce carbon emissions by 5%. That equates to local air quality benefits of roughly 0.2% of<br />

world GDP, or $56 billion for 2000. These estimates, however, depend critically on the<br />

assumptions made about the monetary value of health improvements. A 1995 IEA study<br />

estimated that elim<strong>in</strong>at<strong>in</strong>g all subsidies <strong>in</strong> Russia would reduce NOx emissions by 40% over<br />

20 years compared with 1990 levels. SO2 emissions would fall by 65% and total suspended<br />

particulates by 75%. These would generate substantial air-quality benefits.<br />

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