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L. Kutnar, A. Kobler: PREDICTION OF FORESTVEGETATION SHIFT DUE TO DIFFERENT ... Šumarski list br. 3–4, CXXXV (2011), 113-126


Climate change scenarios –Scenariji klimatskih promjena


For simulation of future vegetation states, the existing
climate-change predictions for Slovenia have
been used (Bergant 2007,Kutnar etal. 2009).To
estimate the future temperature and precipitation conditions
in different regions of Slovenia by the end of
the 21st
century, empirical downscaling was used to
project the results of General Circulation Model
(GCMs) simulations with four different models
(CSIRO/Mk2, UKMO/HadCM3, DOE-NCAR/PCM
in MPI-DMI/ECHAM4-OPYC3) to five selected locations
in Slovenia (Ljubljana, Novo Mesto, Murska Sobota,
Rateče-Planica in Bilje) (Bergant 2007). A
combination of empirical orthogonal function analysis
together with a partial least squares regression was
used to develop empirical models based on local observations
and NCEP/NCAR reanalysis in the large scale.


Spatial model –


Within the present forest area, a model was constructed,
linking the vegetation type to the climate factors,
the relief and the soil at the spatial level of
100×100 m quadrants, in order to provide the model-
based predictions of potential vegetation distribution in
case of climate warming.The relationship was gleaned
with the data mining tool SEE5 (www.rulequest.com)
from the empirical data (training dataset).The training
data consisted of equal numbers of randomly sampled
records for each vegetation type. Each record consisted
of the current vegetation type at a particular 100×100 m
quadrant, followed by the corresponding climate data
(average monthly and yearly temperature, precipitation
and evapotranspiration values for the 1970–2000 period),
relief data (elevation, terrain slope, terrain exposition),
and soil data (FAO soil type). The model
constructed with SEE5 took the form of a decision tree.
The accuracy of the model was estimated to be 71% (at
the level of 13 vegetation types) with 10-fold cross-validation
on training data. The cross-validation returns
As GCM simulations are commonly based on a limited
number of emission scenarios, in this case SRESA2
and B2, local projections were additionally scaled to
other marker SRES scenarios (A1Fl,A1T,A1B).The
results of projections indicate the strongest warming in
summer(3.5 °C to 8°C) followed by winter (3.5°C to
7°C), spring (2.5°C to 6°C), and autumn (2.5°C to
4°C) (Bergant 2007). No significant change in precipitation
amounts is expected in spring and autumn,
while in summer a decrease in precipitation (-20%) and
in winter an increase (+30%) is expected.


For the simulation of changes of potential forest vegetation,
the existing climate-change predictions for
Slovenia (Bergant 2007) have been used to create
three different scenarios.


Prostorni model


similar accuracy values as the validation using an independent
control sample. Using the model and the existing
predictions of the likely future climate (Bergant
2007), we predicted the shift of the forest vegetation in
Slovenia for the years 2040, 2070 and 2100 under three
climatic scenarios: the mean scenario (median predicted
temperature T, median predicted precipitation R,
median predicted evapotranspiration E), the pessimistic
scenario (maxT,min R, max E), and the optimistic scenario
(minT, max R, min E). For comparisons of the
predicted values to the present values, we used the potential
present values, i.e. modelled present values, and
not the real present values. Therefore, the differences
between the present and the predicted values were less
influenced by the errors of the model. Since the empirical
model is only valid within the present forest area, it
cannot predict change of the forest area due to climate
warming. Therefore, our predictions of vegetation
change were only made within the present confines of
the forests.


RESULTS – Rezultati


Taking into consideration the future climate changes
(defined by three different climate scenarios: the
mean scenario, the pessimistic scenario and the optimistic
scenario), the simulation of the future potential forest
vegetation showed significant changes of
vegetation-type shares in Slovenia. By using all three
climate scenarios in an empirical GIS model, the simulations
showed the alteration of spatial pattern of 13 vegetation
types (groups of similar forest communities)
under impacts of climate vary considerably (Figure 2).


The mesic forest vegetation may be adversely af


fected by such changing environmental conditions.


The decrease of the share of currently prevailing beech
vegetation types, e.g. groups of Acidophilic Fagus


sylvatica forests (14.2%), of Submontane Fagus
sylvaticaforests (13.0%), and (Alti-) montaneFagus
sylvatica forest in (Pre-)Dinaric region (11.2%),
could be expected (Table 1). By the year 2100, the
share ofAcidophilicFagus sylvaticaforests might be
decreased to range between 0.0% (pessimistic scenario)
and 5.0% (optimistic scenario); and the share of
Submontane Fagus sylvatica forests might be contracted
to range between 0.0% and 4.0% (Table 1).
The constant decreasing of (Alti-)montane Fagus
sylvatica forest in the (Pre-)Dinaric region, among
which Dinaric fir-beech forests (Abieti-Fagetum
dinaricum, sin. Omphalodo-Fa ge tum) prevail, has
been forecast (Graph 1).