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Increasing interannual and altitudinal ozone mixing ratios in the Catalan Pyrenees
Authors:Maria Díaz-de-Quijano  Josep Peñuelas  Àngela Ribas
Institution:1. Research and Innovation Centre, Fondazione Edmund Mach (FEM), Via E. Mach 1, 38010 San Michele all''Adige, TN, Italy;2. TerraData environmetrics, via L. Bardelloni 19, 58025 Monterotondo M.mo, Grosseto, Italy;1. CREAF, Cerdanyola del Vallès 08193, Spain;2. Ecotoxicology of Air Pollution, CIEMAT, Avda. Complutense 22, 28040 Madrid, Spain;3. Forestry Technology Centre of Catalonia (CTFC), St. Llorenç de Morunys km 2, 25280 Solsona, Spain;4. Technical School of Agricultural and Forestry Engineering, University of Castilla la Mancha, Campus Universitario s/n, 02071 Albacete, Spain;5. CSIC, Cerdanyola del Vallès 08193, Spain;6. Terrestrial Ecology Group, Animal Biology and Ecology Department, University of Granada, E-18071 Granada, Spain;7. Institute of Environmental Assessment and Water Research (IDAEA), CSIC, 08034 Barcelona, Spain;8. Universitat Autònoma de Barcelona, Cerdanyola del Vallès 08193, Spain;9. Animal Biology Area, Environmental Sciences Department, University of Girona, Campus Montilivi, 17071 Girona, Spain;10. National Museum of Natural Sciences (MNCN), CSIC, Serrano 115 dpdo. E-28006 Madrid, Spain;11. Departamento de Biología y Geología, ESCET, Universidad Rey Juan Carlos, c) Tulipán s/n, 28933 Móstoles, Madrid, Spain;12. Doñana Biological Station (EBD-CSIC), Américo Vespucio s/n, Isla de la Cartuja, 41092 Sevilla, Spain;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
Abstract:Interannual, seasonal, daily and altitudinal patterns of tropospheric ozone mixing ratios, as well as ozone phytotoxicity and the relationship with NOx precursors and meteorological variables were monitored in the Central Catalan Pyrenees (Meranges valley and Forest of Guils) over a period of 5 years (2004–2008). Biweekly measurements using Radiello passive samplers were taken along two altitudinal transects comprised of thirteen stations ranging from 1040 to 2300 m a.s.l. Visual symptoms of ozone damage in Bel-W3 tobacco cultivars were evaluated biweekly for the first three years (2004–2006). High ozone mixing ratios, always above forest and vegetation protection AOT40 thresholds, were monitored every year. In the last 14 years, the AOT40 (Apr–Sept.) has increased significantly by 1047 μg m?3 h per year. Annual means of ozone mixing ratios ranged between 38 and 67 ppbv (38 and 74 ppbv during the warm period) at the highest site (2300 m) and increased at a rate of 5.1 ppbv year?1. The ozone mixing ratios were also on average 35–38% greater during the warm period and had a characteristic daily pattern with minimum values in the early morning, a rise during the morning and a decline overnight, that was less marked the higher the altitude. Whereas ozone mixing ratios increased significantly with altitude from 35 ppbv at 1040 m–56 ppbv at 2300 m (on average for 2004–2007 period), NO2 mixing ratios decreased with altitude from 5.5 ppbv at 1040 m–1 ppbv at 2300 m. The analysis of meteorological variables and NOx values suggests that the ozone mainly originated from urban areas and was transported to high-mountain sites, remaining aloft in absence of NO. Ozone damage rates increased with altitude in response to increasing O3 mixing ratios and a possible increase in O3 uptake due to more favorable microclimatic conditions found at higher altitude, which confirms Bel-W3 as a suitable biomonitor for ozone concentrations during summer time. Compared to the valley-bottom site the annual means of ozone mixing ratios are 37% larger in the higher sites. Thus the AOT40 for the forest and vegetation protection threshold is greatly exceeded at higher sites. This could have substantial effects on plant life at high altitudes in the Pyrenees.
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