Περίληψη σε άλλη γλώσσα
In this doctorate thesis the main biodiversity patterns were investigated at
multiple scales of analysis. There is an increasing need for preserving and
restoring the natural environment due to the continuous degradation caused
by human presence. As study areas were selected the aquatic ecosystems
included in the Natura 2000 network. Three were the levels of biodiversity that
were analyzed for the current study: (a) aquatic ecosystem’s landscape, (b)
aquatic ecosystem’s species (freshwater fish fauna) and (c) aquatic
ecosystem’s habitat types.
At the landscape level, the protected areas including reservoirs were
compared to those including lakes and rivers. The landscape structure and
habitat type composition of reservoirs were completely different to lake and
rivers. The intensity of human presence, as this was measured by the
presence of arable land and settlements did not differ significantly among the
three types of ecosystems. It appeared that reservoir ecosystems wer ...
In this doctorate thesis the main biodiversity patterns were investigated at
multiple scales of analysis. There is an increasing need for preserving and
restoring the natural environment due to the continuous degradation caused
by human presence. As study areas were selected the aquatic ecosystems
included in the Natura 2000 network. Three were the levels of biodiversity that
were analyzed for the current study: (a) aquatic ecosystem’s landscape, (b)
aquatic ecosystem’s species (freshwater fish fauna) and (c) aquatic
ecosystem’s habitat types.
At the landscape level, the protected areas including reservoirs were
compared to those including lakes and rivers. The landscape structure and
habitat type composition of reservoirs were completely different to lake and
rivers. The intensity of human presence, as this was measured by the
presence of arable land and settlements did not differ significantly among the
three types of ecosystems. It appeared that reservoir ecosystems were
completely different, compared to those of lakes and rivers and the
management strategies applied should be different among the three types of
ecosystems. The management bodies should apply different measures for the
preservation and restoration of the unique biodiversity of these ecosystems.
At the species level, the factors determining the composition of native fish
fauna of freshwater ecosystems were determined. In the analysis were
examined local environmental variables, as well as species dispersal ability,
calculated in terms of straight-line Euclidean distances between ecosystems.
The analysis was carried out for aquatic ecosystems occupying a large part of
the country and then for the different biogeographical zones. At both levels,
the importance of species dispersal was greater than that of local
environmental variables. At the country level, species biogeography was the
most important factor determining community composition. It was described
by the routes of dispersion these species followed when inhabiting the Balkan
Peninsula. The natural barriers of seawater and Pindus Range did not allow species dispersal through all freshwater ecosystems of Greece. At the level of
biogeographical zones, species dispersal seemed to be once again the main
factor determining species community composition compared to
environmental parameters. In conclusion, species dispersal ability,
biogeography and the presence of natural barriers determined species
community composition more than environmental variability.
At the habitat type level, the factors determining habitat type composition in
most Greek protected aquatic ecosystems were assessed. The relative
contribution of geographical, spatial and climatic measures was estimated for
the protected aquatic ecosystems of Greece. Climatic variables were the main
determinants of habitat type composition compared to spatial and
geographical parameters. More specifically, precipitation measures and even
more their extreme values were the main determinants of richness patterns,
compared to temperature measures, which seemed to have had a smaller
contribution. The assessment of habitat type richness is of great importance
as it could give an estimate for the effects of climatic conditions on patterns of
biodiversity.
Spatial pattern analysis can provide the possibility for a better estimation,
description and understanding of the structure of an aquatic ecosystem’s
landscape. At the species level it is important for researchers to consider both
species biogeography and dispersal ability, as well as the structure of
landscape matrix. At the habitat type level the role of spatial pattern seemed
to be secondary while the role of climate was the main determinant of
richness patterns. It became apparent that at each level of observation
(aquatic ecosystem, species in the ecosystem and habitat types comprising
the ecosystem’s landscape) the relative contribution of spatial structure,
dispersal limitation and climatic variables, to determining biodiversity patterns
varies.
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