Report - ICP Forests
Report - ICP Forests
Report - ICP Forests
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3. Intensive Monitoring 75<br />
Missing values and correspondence between vegetation and abiotic data<br />
After the exclusion of records with deficient soil data, there are three records without<br />
coordinates (and hence, without climate zone and EMEP deposition estimates). These were also<br />
excluded from the analysis. After these exclusions and the replacement of missing soil data by<br />
estimates, 616 usable records remain with soil, 'other', and EMEP deposition data, and 265 with<br />
soil, 'other', bulk and throughfall deposition data.<br />
Annex 3.4.3 gives the correlation matrix of all variables used in the CCA analysis of last relevé<br />
per plot using EMEP deposition estimates. Other analyses have been carried out on different<br />
subsets of the data and therefore have slightly different correlation matrices; for the correlation<br />
between the EMEP estimates and measured bulk and throughfall deposition see Annex 3.4.2.<br />
On the vegetation side, species with less than three occurrences and relevés with less than three<br />
species were excluded from the multivariate analysis of the last relevé per plot, to avoid a very<br />
heterogeneous data set. This resulted in 598 usable records, of which 477 had usable abiotic data<br />
(excl. bulk and throughfall deposition). These 477 relevés had 170 species (after the exclusion<br />
of very rare ones). A separate analysis was done with the bulk and throughfall deposition data<br />
instead of the EMEP estimates; for this analysis there were 181 usable records containing 114<br />
species. For the analysis of the vegetation change the first and the last relevé of each plot were<br />
used if the interval between them was seven years or more; this yielded 161 plots, of which 138<br />
had usable abiotic data, and 60 bulk deposition and throughfall data. In this operation rare<br />
species or species-poor relevés were not excluded because the linear statistical methods used<br />
here are less sensitive to heterogeneity.<br />
3.4.3 Statistical methods<br />
The statistical methods used are similar to those used in 2002 (De Vries et al. 2002). The effect<br />
of the environmental variables on the vegetation of the last relevé of each plot was assessed by<br />
canonical correspondence analysis (CCA). The exclusion of very rare species (< 3 occurrences)<br />
and downweighting of rare species resulted in a gradient length GL 1 = 7.5 and explained<br />
variance λ 1 / Σλ = 4.6% for the first axis at 477 samples and 170 species which was judged<br />
acceptable. The change in the vegetation was determined as (%cover in last relevé) minus<br />
(%cover in first relevé) per species. The significance of this change was determined by ordinary<br />
linear statistics. The relation between the change in the vegetation and the environmental<br />
variables was analysed for all species together using RDA (= the linear form of CCA = the<br />
canonical form of PCA). Ellenberg values were determined as the unweighted mean over all<br />
species (incl. the rare species but excl. relevés with < 3 species with a known Ellenberg value).<br />
The relation between the change in Ellenberg values and environmental variables was assessed<br />
using multiple regression. All multivariate operations were carried out by the program<br />
CANOCO v 4.53, all univariate operation by the program GENSTAT v 12.1.<br />
3.4.4 Results<br />
CCA analysis of last relevé per plot<br />
Possible observer effects were assessed by determining the unique contributions ('TMVs') of the<br />
countries and the 'real' environmental variables (Table 3.4.4-1). Out of a total of 25% variance<br />
that can be explained anyway, 5% is uniquely due to the countries. As both the geographical<br />
coordinates and climate zones are among the environmental variables this 'county effect' is most<br />
probably caused by methodological differences. Estonia, France, the Netherlands, Ireland and<br />
Italy are the most deviant countries (in that order) and their effect is significant even after<br />
accounting for the effect of all environmental variables. Therefore the countries were used as<br />
covariables in the subsequent analysis. Table 3.4.4-2 gives the result of the forward selection.<br />
Like in De Vries at el. (2002), the variables were included in the model stepwise, at each step