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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 />

NO x emission to 0.5 Tg N yr -1 (Figure 2-3).<br />

The original 2-D (altitude-latitude) model studies of <strong>the</strong> tropospheric ozone impacts of subsonic NO x emissions are close to <strong>the</strong> (mean + 1xsd) line from <strong>the</strong> entire<br />

ensemble of studies. 2-D model estimates have declined steadily so that by 1992 <strong>the</strong>y were close to <strong>the</strong> (mean - 1xsd) line. The original 1-D studies showed a large<br />

amount of scatter <strong>and</strong> have not been used extensively for assessment purposes for <strong>the</strong> past decade or so. 2-D channel (altitude-longitude) models have been applied<br />

to <strong>the</strong> aircraft assessment as an interim strategy prior to 3-D (altitude-latitude-longitude) model development. 2-D channel model results are toward <strong>the</strong> high end of <strong>the</strong><br />

range of results.<br />

3-D models have been employed increasingly from 1994 onward, with <strong>the</strong> results lying toward <strong>the</strong> low end of <strong>the</strong> overall spread of model results. 3-D model results still<br />

show a considerable amount of scatter, <strong>and</strong> <strong>the</strong>re is no evidence that <strong>the</strong> move from 2-D to 3-D models or <strong>the</strong> selection of 3-D models in Chapter 4 has improved intermodel<br />

consistency or overall predictive confidence. Regardless of how 2-D model results compare with zonally averaged 3-D model results, a crucial advantage of 3-D<br />

models is that <strong>the</strong>y can account for zonal asymmetries <strong>and</strong>, in principle, be evaluated more decisively against local observations. Consequently, more confidence can<br />

be gained in <strong>the</strong>ir predictive capabilities for aircraft assessments (see Sections 2.3.1.1 <strong>and</strong> 2.3.1.2).<br />

Based on all model results compiled for this assessment, our estimate of <strong>the</strong> likely ozone increase at its maximum in <strong>the</strong> principal traffic areas-9-13 km altitude, 30-60°<br />

N latitude-from 1992 subsonic aviation <strong>and</strong> during summer is about 6%, or 8 ppb, for a global aircraft NOx emission of 0.5 Tg N yr-1 (1.65 Tg NOx as NO2 yr-1 ; see<br />

Chapter 9).<br />

Chapter 4 focuses attention on <strong>the</strong> development of future scenarios for subsonic aircraft NOx emissions; six 3-D global models have been employed to assess future<br />

impacts of subsonic aircraft. Table 2-1 shows ozone changes calculated in some of <strong>the</strong>se models for 1992 subsonic operations compared with model results presented<br />

in previous studies. The latest model results in Table 2-1 appear to lie well within <strong>the</strong> central range of estimates from previous studies.<br />

The estimates in Table 2-1 can be compared with previous assessments of <strong>the</strong> likely ozone impacts of NOx emissions from present aviation. The WMO-UNEP (1995)<br />

assessment described model results available to <strong>the</strong> end of 1993 as preliminary <strong>and</strong> indicative of maximum ozone increases of 4-12% at around 10 km for 30-50°N.<br />

The above estimates encompass a narrower range than that given in <strong>the</strong> WMO-UNEP (1995) assessment <strong>and</strong> suggest that <strong>the</strong> true value is at <strong>the</strong> lower end of<br />

previous estimates. An assessment prepared for <strong>the</strong> European Commission (Brasseur et al., 1998) concluded that <strong>the</strong> current fleet of commercial aircraft should have<br />

increased NOx abundances by 50-100 ppt near 200 hPa, with a corresponding increase in ozone concentrations of 5-9 ppb (i.e., 4-8%), during summertime. This latter<br />

range is consistent with <strong>the</strong> range identified in <strong>the</strong> present study, based on <strong>the</strong> five selected 3-D models.<br />

2.2.1.2. Effects of Aircraft NO x Emissions on Stratospheric Ozone<br />

2-D models have been developed extensively over <strong>the</strong> past decade in response to <strong>the</strong><br />

need for credible predictions of CFC impacts on stratospheric ozone <strong>and</strong> more recently for<br />

underst<strong>and</strong>ing <strong>the</strong> effects of future supersonic (high speed civil transport, or HSCT)<br />

aircraft fleets. Emphasis in <strong>the</strong>se models has been placed on ClOx , HOx , <strong>and</strong> NOx chemistry in <strong>the</strong> 20-40 km region of <strong>the</strong> atmosphere, where <strong>the</strong> CFC <strong>and</strong> HSCT effects<br />

are expected to be manifested. Model calculations for <strong>the</strong> 1992 subsonic aircraft fleet<br />

http://www.ipcc.ch/ipccreports/sres/aviation/026.htm (4 von 6)08.05.2008 02:41:43

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