Critical levels of SO2 - uncertainty and relationships to Regional Forest Decline

Three methods estimating adverse effects of SO2 on Norway spruce forests were applied and evaluated on a regional level in northern Czech Republic. The methods, assuming adverse effects to occur when predetermined thresholds are exceeded, include the critical level of SO2 concentration (1), the ratio of the SO2 concentration to the vegetation period (SO2/VP) (2) and a model predicting needle loss from environmental data and SO2 (3). Comparing the estimated impact with observed regional forest decline reveals significant relationships for all methods. The influence of data uncertainty, quantified using Monte Carlo simulation, was used to map areas significantly over or below the critical thresholds. The main results show: (1) that there are strong linear relationships between accumulated salvage fellings and the SO2 concentrations, the SO2/VP ratio and a model predicting needle loss in response to elevated SO2 concentrations, (2) there is a clear relationship between damage classes based on defoliation and SO2 concentration. A critical value of 20 [mug m - 3 yr - 1] (mean annual concentration) seems a reasonable choice to distinguish between no effects below this level and possible effects above this level. The same is true for the SO2/VP ratio of 0.07 [nPa Pa - 1 day - 1]. The results indicate no substantial contribution from the increased structural complexity and data demand for methods 2 and 3. High quality SO2 data with known uncertainty and integration with high - resolution land cover data are the main requirements for improved mapping and identification of various receptors at risk. (Less)

[1]  S. Slovik Early needle senescence and thinning of the crown structure of Picea abies as induced by chronic SO2 pollution. II. Field data basis, model results and tolerance limits , 1996 .

[2]  S. Slovik Early needle senescence and thinning of the crown structure of Picea abies as induced by chronic SO2pollution. I. Model deduction and analysis , 1996 .

[3]  W. Kaiser,et al.  SO2‐dependent cation competition and compartmentalization in Norway spruce needles , 1996 .

[4]  J. Fuhrer,et al.  Establishing critical levels for the effects of air pollution on vegetation , 1995 .

[5]  Jonas Ardö,et al.  Spectral characterization and regression-based classification of forest damage in Norway spruce stands in the Czech Republic using Landsat Thematic Mapper data , 1995 .

[6]  V. Hynek,et al.  Life expectancy of spruce needles under extremely high air pollution stress: performance of trees in the Ore Mountains , 1994, Trees.

[7]  J. Kopáček,et al.  Sulphur air-pollution assessment based on Charles University model;Regionale Ausbreitung und Deposition von Schwefeloxyden — Ein Modell, entwickelt an der Prager Karls-Universität , 1994 .

[8]  P. Moravčík Development of new forest stands after a large scale forest decline in the Krušné hory Mountains , 1994 .

[9]  E. Führer Forest decline in central Europe: Additional aspects of its cause , 1990 .

[10]  J. Materna Air pollution and forestry in czechoslovakia , 1989, Environmental monitoring and assessment.

[11]  W. Beyschlag,et al.  Photosynthetic performance and nutrient status of Norway spruce [Picea abies (L.) Karst.] at forest sites in the Ore Mountains (Erzgebirge) , 2004, Trees.

[12]  Peter Schlyter,et al.  Uncertainties in high resolution critical load assessment for forest soils- possibilities and constraints of combining distributed soil modelling and GIS. , 1999 .

[13]  Jonas Ardö,et al.  Satellite Based Estimations of Coniferous Forest Cover Changes : Krusne Hory, Czech Republic , 1997 .

[14]  W. Vries,et al.  Calculating critical loads for acidity with the simple mass balance method , 1994 .

[15]  J. Nilsson,et al.  Critical Loads for Sulphur and Nitrogen , 1988 .

[16]  E. Davison Forest decline in Central Europe , 1988 .