Abstract

ESCOMPTE programme aims at studying the emissions of primary pollutants in industrial and urban areas, their transport, diffusion and transformation in the atmosphere. This experiment, carried out in southeast France, can be used to validate and to improve meteorological and chemical mesoscale models. One major goal of this experiment was to follow the pollutant plumes, and to investigate its thermodynamic and physico-chemical time evolution. This was realized by means of constant volume balloons, located by global position satellite (GPS) and equipped with thermodynamic and ozone sensors, flying at constant density levels. During the two ESCOMPTE campaigns that took place in June and July 2000 and 2001, 40 balloons were launched, 17 of them equipped with ozone sensors during the day from 0800 to 1800 UTC. Balloons’ altitudes flight levels ranged between 400 and 1200 m altitude with Mistral (northerly synoptic flow) and Sea Breeze (southerly breeze) conditions. The atmospheric boundary layer (ABL) topography of the experimental domain is complex and varies strongly from day to day. Its depth presents a large gradient from the sea coast to the north part of the ESCOMPTE domain, and also more complex variability within the domain. The balloons’ trajectories describe the evolution of the pollutant plume emitted from the industrial area of Fos-Berre or from the Marseille urban area. Constant volume balloons give a good description of the trajectories of these two plumes. The balloons, which fly at an isopicnic level, cross different atmospheric layers chiefly depending on the ABL height in relation with the constant volume balloons flight level. Thus, each balloon flight is decomposed into different segments that correspond to the same atmospheric layer. In each segment, the ozone content variation is analyzed in relation to other thermodynamical parameters measured by the balloon and mainly to the vapor mixing ratio content. During ESCOMPTE campaign, the mean linear rate of chemical net ozone production at the top of the atmospheric boundary layer was found to be around 6 ppb h −1.

Highlights

  • The expanding industrialisation and rapidly growing mobility of the human society during the past 30 years are producing an increase in tropospheric ozone concentration that has doubled in urban and peri-urban areas around the world (Volz and Kley, 1988)

  • We present original results concerning quasi-Lagrangian measurements of ozone concentrations obtained with instruments, near the atmospheric boundary layer (ABL) top and in the stable layers of the free atmosphere just above the ABL

  • The balloon flight altitude has been systematically compared with the ABL top along its trajectory

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Summary

Introduction

The expanding industrialisation and rapidly growing mobility of the human society during the past 30 years are producing an increase in tropospheric ozone concentration that has doubled in urban and peri-urban areas around the world (Volz and Kley, 1988). During the socalled summer smog episodes caused by high-pressure weather conditions, ozone concentration in the polluted continental boundary layer exhibits at the surface a pronounced diurnal cycle with a maximum during the day and a minimum at night. Turbulent mixing and photochemical activity are the main sources of ozone variability in the low layers of the troposphere. The nocturnal residual layer of the atmospheric boundary layer (ABL) acts as an ozone reservoir. Diurnal CBL growth plays an important role in the morning increase of surface ozone measurements as it has been analyzed for example by Baumbach and Vogth (2003)

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