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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 />

Representation of heterogeneous processes on cold aerosols (PSCs) is not consistent among <strong>the</strong> participating models (Sections 4.3.1.3 <strong>and</strong> 4.3.3.5.). These<br />

differences are manifest when increased abundances of NO Y <strong>and</strong> H 2 O from supersonic aircraft are considered. As mentioned previously, <strong>the</strong> transport fields of<br />

participating assessment models are significantly different; <strong>the</strong>refore, <strong>the</strong> amount of supersonic H 2 O <strong>and</strong> NOy dispersion between hemispheres <strong>and</strong> vertically within <strong>the</strong><br />

same hemisphere is also different. Three models (AER, GSFC, <strong>and</strong> UNIVAQ) investigated <strong>the</strong> impact on total O 3 when cold aerosol representation was not included<br />

(S4b). These models removed <strong>the</strong>ir representation of SAD, dehydration, <strong>and</strong> denitrification that would be associated with cold aerosol processes. The results were<br />

mixed. When cold aerosol processes were included in <strong>the</strong> model chemistry formulation, <strong>the</strong> model-derived percentage change in Nor<strong>the</strong>rn Hemisphere total column O3 increased by factors of 1.1 <strong>and</strong> 1.5 for <strong>the</strong> GSFC <strong>and</strong> AER models, respectively (S1c vs. S4b). However, in <strong>the</strong> Sou<strong>the</strong>rn Hemisphere <strong>the</strong> GSFC model-derived<br />

depletion in total O3 increased by 2.5 when cold chemistry processes were included. There was minimal change in Sou<strong>the</strong>rn Hemisphere average O3 depletion in <strong>the</strong><br />

AER model. When <strong>the</strong> EI(NO x ) is set to zero (S4a), a similar conclusion is also drawn (compare to S1b) by <strong>the</strong> AER <strong>and</strong> GSFC models. These results are consistent<br />

with <strong>the</strong> dispersion of supersonic H2O <strong>and</strong> NOy between <strong>the</strong> AER <strong>and</strong> GSFC models. The UNIVAQ model did show sensitivity to supersonic emissions in <strong>the</strong> total O3 hemispheric averages; because <strong>the</strong> absolute impact was small <strong>and</strong> centered around zero, however, it is difficult to draw any significant conclusions.<br />

4.3.3.6. Ambient Chlorine Sensitivity<br />

Total radical chlorine (Cl y ) abundance in <strong>the</strong> atmosphere is predicted to decrease in <strong>the</strong> future as a result of international agreements controlling production of<br />

anthropogenic organic source gases such as chlorofluorocarbons (CFCs) <strong>and</strong> hydrochlorofluorocarbons (HCFCs) (WMO 1995, 1999). Therefore, several sensitivity<br />

studies were performed to investigate <strong>the</strong> impact of ambient Cl y levels on a given supersonic aircraft perturbation. Here, atmospheric chlorine amounts were varied by<br />

changing halocarbon boundary conditions. Four different ground halocarbon amounts were considered, which resulted in reactive Cl y levels of 1.0, 2.0, 3.0, <strong>and</strong> 4.0<br />

ppbv in <strong>the</strong> upper stratosphere. For reference, <strong>the</strong> 3.0 <strong>and</strong> 2.0 ppbv Cl y levels are representative of predicted 2015 <strong>and</strong> 2050 atmospheric conditions, respectively. In<br />

all Cl y sensitivity studies, only EI(NO x )=5 <strong>and</strong> a fleet of 500 supersonic aircraft were considered. Sensitivity studies were conducted under volcanically clean conditions<br />

without aircraft sulfur emissions (SA0) <strong>and</strong> with sulfur emissions assuming 50% SO 2 gas-to-particle conversion in <strong>the</strong> plume (SA1). Without aircraft sulfur emissions,<br />

<strong>the</strong>re was little discernible sensitivity to background Cl y abundance (S1c, S5a, S6a, <strong>and</strong> S9a). With sulfur emissions included, however, total ozone depletion for all<br />

three participating models was smallest when Cl y abundance was 1.0 ppbv. As Cl y increased in abundance, <strong>the</strong> model-derived ozone depletion increased, maximizing<br />

<strong>and</strong> leveling off between 3.0 <strong>and</strong> 4.0 ppbv Cl y (S1f, S5b, S6b, <strong>and</strong> S9c). Among <strong>the</strong> participating models, AER showed <strong>the</strong> most sensitivity to Cl y abundance, followed<br />

by GSFC <strong>and</strong> UNIVAQ. It should be noted that <strong>the</strong> Cl y =2 ppbv scenario (S9c) had N 2 O <strong>and</strong> CH 4 boundary conditions consistent with <strong>the</strong> year 2050. The o<strong>the</strong>r three<br />

Cl y sensitivity scenarios (S1f, S5b, <strong>and</strong> S6b) had N 2 O <strong>and</strong> CH 4 abundances consistent with <strong>the</strong> year 2015. The AER model did investigate Cl y sensitivity to N 2 O <strong>and</strong><br />

CH 4 boundary conditions by repeating <strong>the</strong> Cl y =2.0 ppbv scenario with N 2 O <strong>and</strong> CH 4 values representative of 2015 conditions. The model-derived change in NH total<br />

O 3 was -0.6% (instead of -0.7% under 2050 CH 4 <strong>and</strong> N 2 O conditions).<br />

4.3.3.7. Fleet Design<br />

4.3.3.7.1. Supersonic cruise altitude sensitivity<br />

http://www.ipcc.ch/ipccreports/sres/aviation/050.htm (8 von 10)08.05.2008 02:42:29

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