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Aviation and the Global Atmosphere

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<strong>Aviation</strong> <strong>and</strong> <strong>the</strong> <strong>Global</strong> <strong>Atmosphere</strong><br />

. Uncertainties about future trends in technology, underlying trends in traffic growth, <strong>and</strong> aircraft fleet mix. This uncertainty is illustrated by recently revised<br />

projections for fleet NO x emission index (EI) made by Boeing for 2015, showing more than a 50% increase from its previous estimate, caused primarily by<br />

reassessment of technology likely to be present in <strong>the</strong> 2015 fleet (Sutkus, 1997).<br />

In addition, uncertainty has arisen regarding whe<strong>the</strong>r new worldwide st<strong>and</strong>ards for aircraft engine emissions would encourage additional local rules by airports <strong>and</strong><br />

governments, leading to a reduction in <strong>the</strong> value of <strong>the</strong> existing aircraft fleet. Two studies reported in <strong>the</strong> economic analysis subgroup (EASG) report to CAEP/3<br />

(EASG, 1995) concluded that emissions stringency options under consideration would lead to a reduction in existing aircraft fleet values for this reason. Some<br />

subsequent studies commissioned by <strong>the</strong> forecasting <strong>and</strong> economic support group (FESG) <strong>and</strong> included in its report to CAEP/4 found that <strong>the</strong> limited quantitative data<br />

available provide inconclusive evidence of any material impact on aircraft fleet values arising from an earlier change in <strong>the</strong> worldwide emissions stringency st<strong>and</strong>ard<br />

agreed at CAEP/2 for NO x (ICAO, 1998a).<br />

CBA may have to be applied somewhat differently in <strong>the</strong> context of environmental levies. All environmental mitigation measures aim to internalize external costs, but<br />

environmental levies achieve this internalization more explicitly <strong>and</strong> to a greater degree. External costs arise where, for example, <strong>the</strong> cost of pollution from an<br />

economic activity does not accrue to <strong>the</strong> party responsible for it. Placing monetary values on external costs may eliminate <strong>the</strong> need for CBA, so <strong>the</strong> focus of economic<br />

analysis can be compliance costs, economic distortion, <strong>and</strong> <strong>the</strong> environmental effectiveness of alternatives. With aircraft emissions, however, <strong>the</strong> monetary value of<br />

<strong>the</strong>se external costs is subject to a wide range of uncertainty, as discussed in Section 10.4.3. In <strong>the</strong>se circumstances-<strong>and</strong> in particular under a regime of emissions<br />

targets introduced on <strong>the</strong> basis of <strong>the</strong> precautionary principle-CBA techniques will be necessary in providing assistance to decisionmakers on <strong>the</strong> most economically<br />

efficient means of meeting such targets.<br />

10.3.3. Elasticity of Dem<strong>and</strong> Considerations<br />

The extent to which cost increases arising from environmental mitigation policies are passed on to consumers <strong>and</strong> affect dem<strong>and</strong> for aviation services depends on<br />

elasticity of dem<strong>and</strong> (<strong>the</strong> responsiveness of consumers to fare increases).<br />

Evidence regarding fare elasticities is particularly relevant in considering <strong>the</strong> impact of environmental levies (charges or taxes) that directly increase <strong>the</strong> cost of air<br />

travel. If dem<strong>and</strong> is relatively unresponsive to fare increases (i.e., price is inelastic), such measures will have little impact in reducing emissions through dampening of<br />

dem<strong>and</strong>. Conversely, if passenger responsiveness is high (i.e., price is elastic), policy measures will have a greater impact. This analysis can be illustrated as follows:<br />

A fare elasticity of -0.5 would mean that a 10% increase in fares would result in a 5% reduction in traffic volume; a fare elasticity of -2.0 would mean that a 10% fare<br />

increase would reduce traffic by 20%.<br />

Estimates of fare elasticities differ by journey purpose; leisure travel generally is significantly more price elastic than business travel. Fare elasticities also exhibit some<br />

regional variation; for example, studies show comparatively higher price elasticities in North America than in o<strong>the</strong>r regions of <strong>the</strong> world. A study commissioned by <strong>the</strong> U.<br />

S. Federal <strong>Aviation</strong> Administration (FAA) (U.S. Department of Transportation, 1995) reviewed more than 25 price elasticity studies <strong>and</strong> found that most presented<br />

elasticity of dem<strong>and</strong> estimates in <strong>the</strong> range of -0.8 to -2.7.<br />

Studies examining <strong>the</strong> effectiveness of environmental levies have had to make assumptions about <strong>the</strong> reaction of airlines <strong>and</strong> how <strong>the</strong> dem<strong>and</strong> for air transport<br />

changes in response to a change in fare. Many commentators agree that in <strong>the</strong> long term, in addition to encouraging more energy-efficient technological alternatives,<br />

an increase in <strong>the</strong> price of fuel will lead to an increase in <strong>the</strong> cost of travel <strong>and</strong> consequent reduction in dem<strong>and</strong>. However, airlines operate in a highly competitive<br />

environment, <strong>and</strong> in <strong>the</strong> short term many may absorb fare increases at a cost to profitability ra<strong>the</strong>r than pass <strong>the</strong>m on to passengers.<br />

http://www.ipcc.ch/ipccreports/sres/aviation/152.htm (3 von 4)08.05.2008 02:44:42

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