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Ozone at the intensive monitoring plots in South-Western European forests: levels, risks, actual and potential effectsRationale
Ozone (O3) is the most important regional air pollutant that may impact forest vegetation in Europe and elsewhere (e.g. Fowler et al., 1999). Current O3 levels and model predictions, together with a series of field and experimental evidences, seem to support the above concern. Yet, "especially the lack of ozone data is a serious limitation" for the EU Intensive Monitoring (Level II) database (De Vries, 2000, p. 27) and it is a considerable scientific and political shortcoming in a program aimed to investigate air pollution effects on forests. Besides the obvious connections with the potential effects on forests, the same strategy document of the EC and UN/ECE intensive monitoring reports the relevance of O3 data also in relation to other themes which were subjected to important political agreement, like the tropospheric chemistry changes and the regional ozone formation (see e.g. the CLRTAP multi-pollutant, multi-effect directive; the Un Biodiversity Convention; the EU Habitat Directive; the EU acidification strategy, the UN/ECE CLRTAP, the EU Air Quality directive) (De Vries, 2000, p. 19). While atmospheric O3 monitoring is still optional under the EU Level II program, various countries are currently measuring O3 at their intensive monitoring plots: for example France, Italy, Spain and Switzerland are measuring O3 concentrations by means of e.g. passive samplers. Passive samplers are useful to get an idea about mean weekly/fortnightly O3 levels, but they do not provide indication about e.g. AOT40 values, i.e. the exposure indicator currently adopted to estimate the potential risk for forests as well as natural vegetation and crops (Fuhrer et al, 1997), nor about the actual vegetation O3 uptake. However, some work has been done to estimate O3 concentrations under complex terrain condition as function of altitude and daytime (e.g. Loibl et al., 1994) and this provide the basis for calculating AOT40 (Level I) values starting from e.g. weekly mean values obtained by passive samplers. However, it is widely recognised that plant response is actually more closely related to the internal ozone dose i.e. the ozone taken into the plant through the stomata, which in turn depends on a variety of ecological factors. Recently, considerable progresses has been done to estimate AOT40 Level II values (an expression of exposure that incorporates the factors modifying the response of plants to ozone, thus providing an estimation of the actual O3 uptake by plants) (Emberson et al., 1998, 2000; Simpson et al., 2000) or other exposure indices (e.g. Grünhage et al., 2001) that may provide more reliable estimates of the actual risk due to O3.
Project aimsThe project addresses an important ecological, scientific and political issue not yet addressed in the 2000-2005 strategy plan for data evaluation suggested by the Forest Intensive Monitoring Coordinating Institute (FIMCI). The project will concentrate on the objectives listed below:
Methods
Work planThe following working packages have been identified:
DataOzone data (WP1, WP2, WP3) Response indicators data (NFCs):
Predictors data:
ResultsThis study investigated “Ozone at the intensive monitoring plots in South-Western European Forests – Levels, risk, actual and potential effects”. Ozone (O3) concentration was measured by passive sampling at 83 forest monitoring sites in France, Italy, Spain and Switzerland. Distinct latitudinal and altitudinal trends are detected. On the basis of passive sampling, cumulated exposure AOT40 was estimated and results show that exceedance of the critical level (either the “old” 10 ppm*h and the “new” 5 ppm*h) occur at the majority of the investigated sites. An attempt to model stomatal O3 flux was undertaken: the results are realistic and Participants
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