『Abstract
A critical load data base was developed for Europe and Northern
Asia using the latest data bases on soils, vegetation, climate
and forest growth. Critical loads for acidity and nutrient nitrogen
for terrestrial ecosystems were computed with the Simple Mass
Balance model. The resulting critical loads are in accordance
with critical loads from previous global empirical studies, but
have a much higher spatial resolution. Critical loads of acidity
are sensitive to both the chemical criterion and the critical
limit chosen. Therefore a sensitivity analysis of critical loads
was performed by employing different chemical criteria. A critical
limit based on an acid neutralizing capacity (ANC) of zero resulted
in critical loads that protect ecosystems against toxic concentrations
of aluminium and unfavourable Al/Bc ratios, suggesting that ANC
could be an alternative to the commonly used Al/Bc ratio. Critical
loads of nutrient nitrogen are sensitive to the specified critical
nitrate concentrations, especially in areas with a high precipitation
surplus. If limits of 3-6 mg N l-1 are used for Western
Europe instead of the widely used 0.2 mg N l-1, critical
loads double on average. In low precipitation areas, the increase
is less than 50%. The strong dependence on precipitation surplus
is a consequence of the simple modelling approach. Future models
should explore other nitrogen parameters (such as nitrogen availability)
instead of leaching as the factor influencing vegetation changes
in terrestrial ecosystems.
Keywords: Critical loads; Acidification; Eurasia; Soil and land
cover; Uncertainties; Equivalent criteria』
1. Introduction
2. Methods
2.1. The critical load model
2.2. Chemical criteria
2.3. Geographical data bases
2.4. Meteorology and hydrology
2.5. Base cation deposition and weathering
2.6. Nutrient uptake, nitrogen immobilization and denitrification
2.7. Al-H relationship and organic acids
3. Results
3.1. Input data
3.2. Critical loads of acidity (sulphur)
3.3. Critical loads of N
3.4. Sensitivity of critical loads
3.4.1. sensitivity to the selection of receptors
3.4.2. Sensitivity to criteria
Critical load of acidity
Critical load for eutrophication
4. Discussion and conclusions
Acknowledgement
Open access
Appendix
Simple mass balance (SMB) models
Critical load of nutrient nitrogen
Critical loads of acidity
Derivation of the critical ANC leaching
References