Abstract

Abstract. In this work we focus on the direct radiative forcing (RF) of black carbon (BC) and sulphuric acid particles emitted by future supersonic aircraft, as well as on the ozone RF due to changes produced by emissions of both gas species (NOx, H2O) and aerosol particles capable of affecting stratospheric ozone chemistry. Heterogeneous chemical reactions on the surface of sulphuric acid stratospheric particles (SSA-SAD) are the main link between ozone chemistry and supersonic aircraft emissions of sulphur precursors (SO2) and particles (H2O–H2SO4). Photochemical O3 changes are compared from four independent 3-D atmosphere-chemistry models (ACMs), using as input the perturbation of SSA-SAD calculated in the University of L'Aquila model, which includes on-line a microphysics code for aerosol formation and growth. The ACMs in this study use aircraft emission scenarios for the year 2050 developed by AIRBUS as a part of the EU project SCENIC, assessing options for fleet size, engine technology (NOx emission index), Mach number, range and cruising altitude. From our baseline modeling simulation, the impact of supersonic aircraft on sulphuric acid aerosol and BC mass burdens is 53 and 1.5 μg/m2, respectively, with a direct RF of −11.4 and 4.6 mW/m2 (net RF=−6.8 mW/m2). This paper discusses the similarities and differences amongst the participating models in terms of changes to O3 precursors due to aircraft emissions (NOx, HOx,Clx,Brx) and the stratospheric ozone sensitivity to them. In the baseline case, the calculated global ozone change is −0.4 ±0.3 DU, with a net radiative forcing (IR+UV) of −2.5± 2 mW/m2. The fraction of this O3-RF attributable to SSA-SAD changes is, however, highly variable among the models, depending on the NOx removal efficiency from the aircraft emission regions by large scale transport.

Highlights

  • In this study we have shown results for four independent chemical-transport models used to assess the impact of a future supersonic aircraft fleet on the chemical composition of the stratosphere

  • The climate impact is quantified in terms of the radiative forcing metric

  • For the aerosols we have calculated both the direct forcing and indirect forcing produced by changes in chemical species (i.e. O3) affected by heterogeneous chemical processes on www.atmos-chem-phys.net/8/4069/2008/

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Summary

Introduction

The growth of the world economy is leading to a rapid expansion of aviation, due to the increasing demand for intercontinental transportation: total aviation emissions have increased and are projected to increase by 3% per year in the future (IPCC, 1999). 747 17.15 0.69 17.84 are 393 Tg/yr, 12.97 g/Kg for the year 2025 and 677 Tg/yr, 10.85 g/Kg for the year 2050 (i.e. scenario S4 in Table 1), to be compared with 2000 reference values of 169 Tg/yr, 12.78 g/Kg (Grewe and Stenke, 2008) This means that the SCENIC projected average increase of fuel use is about 3.4% up to 2025 and 2.8% up to 2050, both consistent with the 3% estimate in IPCC (1999), taking into account the projected greater efficiency of future aircraft. Aircraft emit both gases and particles (CO2, NOx, H2O, CO, hydrocarbons, black carbon and sulphate aerosols) directly into the upper troposphere and lower stratosphere (UT/LS region), where they have an impact on the atmospheric composition.

ULAQ-CTM
SLIMCAT
OsloCTM2
Validation with stratospheric aerosol observations
Mass and surface area density
Size distribution
Radiative forcing
Chemistry
Findings
Conclusions
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