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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 />

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

Table of contents | Previous page | Next page<br />

9.4.1.2. FESG Technology Projections<br />

O<strong>the</strong>r reports in this collection<br />

Calculations of fuel burned <strong>and</strong> NO x emissions produced by <strong>the</strong> 2050 scheduled fleet were made by applying projections of overall improvement in fleet fuel efficiency<br />

<strong>and</strong> emission characteristics to regional traffic flows <strong>and</strong> summing <strong>the</strong> results. These projections were created from technology-level estimates for new aircraft over<br />

time made by a working group of <strong>the</strong> International Coordinating Council of Aerospace Industries Associations (ICCAIA) (Sutkus, 1997); <strong>the</strong>y are discussed in Section<br />

7.5.5. A "fleet rollover" model was used to project a fleet average fuel efficiency trend, using characteristics of <strong>the</strong> present-day fleet <strong>and</strong> traffic dem<strong>and</strong> from <strong>the</strong> FESG<br />

scenarios (Greene <strong>and</strong> Meisenheimer, 1997). The ICCAIA projections were made for two technology scenarios. The first scenario assumes that fuel efficiency <strong>and</strong><br />

NO x reduction will be considered in <strong>the</strong> design of future aircraft in a manner similar to <strong>the</strong> current design philosophy. The second technology scenario assumes a more<br />

aggressive NO x reduction design strategy that will result in smaller improvements in fuel efficiency. The assumptions associated with <strong>the</strong> two technology scenarios are<br />

given in Table 9-11. The basis for projections of aircraft emissions made by FESG for <strong>the</strong> year 2050 was <strong>the</strong> 3-D NASA emissions scenarios for <strong>the</strong> year 2015<br />

discussed in Section 9.3.2. The NASA 2015 emissions inventory was factored on <strong>the</strong> basis of <strong>the</strong> product of <strong>the</strong> ratios of regional traffic (as departures), fleet fuel<br />

efficiency, <strong>and</strong> fleet EI(NO x ) as calculated for 2050 over <strong>the</strong> same values in 2015. For all flights in a given region:<br />

NOx Emissions2050 = NOx Emissions2015 (regional traffic2050 / regional traffic2015 )<br />

(fleet fuel efficiency 2050 / fleet fuel efficiency 2015 )<br />

(fleet EI(NO x ) 2050 / fleet EI(NO x ) 2015 )<br />

Figure 9-18 shows <strong>the</strong> trend for average new production <strong>and</strong> fleet average fuel efficiency as a function of time, derived from ICCAIA inputs <strong>and</strong> <strong>the</strong> fleet rollover model<br />

for <strong>the</strong> FESG high-dem<strong>and</strong> traffic growth scenario. The average NOx emission index for <strong>the</strong> scheduled fleet over <strong>the</strong> same time period is shown in Figure 9-19. The<br />

2050 fleet average values used in <strong>the</strong> calculation of emissions from scheduled traffic as well as <strong>the</strong> baseline 2015 value are given in Table 9-12 (Sutkus, 1997). Fleet<br />

fuel efficiency is predicted to improve by about 30% between 2015 <strong>and</strong> 2050. Traffic in <strong>the</strong> FSU <strong>and</strong> <strong>the</strong> People's Republic of China has not historically been reported<br />

http://www.ipcc.ch/ipccreports/sres/aviation/139.htm (1 von 5)08.05.2008 02:44:25

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