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Variability of ozone concentration in a montane environment,northern Italy
Authors:Elena Gottardini  Antonella Cristofori  Fabiana Cristofolini  Marco Ferretti
Institution:1. Fundación CEAM, c/ Charles R. Darwin, 14, Parque Tecnológico, Paterna 46980, Spain;2. ACRI-HE, 260 route du Pin Montard, 06904 Sophia-Antipolis Cedex, France;3. Swiss Federal Research Institute WSL, Zuercherstrasse 111, 8903 Birmensdorf, Switzerland;4. ENEA, CR Casaccia, Via Anguillarese 301, Roma, Italy;1. Technische Universität München, Section of Forest Genetics, Hans-Carl-von-Carlowitz-Platz 2, 85354 Freising, Germany;2. Helmholtz Zentrum München, Institute of Biochemical Plant Pathology, Ingolstädter Landstraße 1, 85764 Neuherberg, Germany;3. University Children''s Hospital (UKBB) at University of Basel, Spitalstrasse 33, 4031 Basel, Switzerland;4. Université de Bordeaux, Centre de Génomique Fonctionnelle, Plateforme Protéome Bordeaux, 33000 Bordeaux, France;5. Technische Universität München, Ecophysiology of Plants, Department of Ecology and Ecosystem Sciences, Hans-Carl-von-Carlowitz-Platz 2, 85354 Freising, Germany;6. Helmholtz Zentrum München, Institute of Biochemical Plant Pathology Research Unit Environmental Simulation, Ingolstädter Landstraße 1, 85764 Neuherberg, Germany;7. Helmholtz Zentrum München, Institute of Soil Ecology, Ingolstädter Landstraße 1, 85764 Neuherberg, Germany;8. Endothelial Cell Biology Unit, School of Molecular & Cellular Biology, LIGHT Laboratories, and Department of Applied Mathematics, School of Mathematics, University of Leeds, Leeds LS2 9JT, United Kingdom
Abstract:To evaluate the spatial variability of ozone concentrations, two studies were undertaken in the montane environment of Trentino region, northern Italy, in 2007. In the first study, a 225 km2 area was considered. Here, a randomized design was used to evaluate the variability of ozone concentration at 1 and 225 km2 scale. Measurements were carried out by passive samplers between May and June 2007. In a second study, the whole 6207 km2 area of Trentino was considered. The area is covered by five grid cells of the European Monitoring and Evaluation Programme (EMEP). A systematic 15 × 15 km grid was used to allocate 15 passive samplers over the entire province, resulting into 1–4 samplers for each of the 5 EMEP grid cells (2500 km2 each) overlapping the study area. Measurements were carried out between June and September 2007. Accuracy of passive samplers was checked by direct comparison with conventional ozone analysers. Significant differences (P = 0.034) were found in ozone concentration among 1 × 1 km quadrates within the 225 km2 study area, while variability within the 1 × 1 km grid cells (coefficient of variation, CV′ = 0.12) slightly exceed the measurement error (CV′ = 0.08). At larger scales (225, 2500 and 6207 km2), ozone concentration shows much higher variability (CV′ from 0.18 to 0.28, with peak values at 0.40). Reported differences lead to very different AOT40 estimates even within the same EMEP grid cell. These findings suggest that 1 × 1 km resolution seems appropriate for ozone concentration modelling. On the other hand, significant sub-grid variation may exist at the resolution adopted by the EMEP model. Coupled with the likely variability of other important meteorological, soil and vegetation variables, our findings suggest that ozone risk assessment for vegetation based on large-scale modelled AOT40 and flux needs to be considered with great caution. The evidence reported in this paper asks for more detailed national-scale modelling, and the development of methods to incorporate local scale variations into large-scale models.
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