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Ecology and regeneration of forest communities on the alluvial fan ...

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-Discussi<strong>on</strong>-<br />

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Fig. 5.3 L<strong>on</strong>gitudial secti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>the</strong> <strong>fan</strong><br />

Direct effects <str<strong>on</strong>g>of</str<strong>on</strong>g> flooding include reduced oxygen exchange <str<strong>on</strong>g>and</str<strong>on</strong>g> hampered soil water<br />

movement (Hughes et al. 2001) uprooting (Karrenberg et al. 2003) as well as burial by<br />

sediments (Marigo et al. 2000). Indirect effects are <strong>the</strong> creati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> bare substrates due to<br />

sedimentati<strong>on</strong> (Johns<strong>on</strong> 2000), decreased vegetati<strong>on</strong> cover <str<strong>on</strong>g>and</str<strong>on</strong>g> increased nutrient supply<br />

(Thoms 2003). The resp<strong>on</strong>se to <strong>the</strong> above menti<strong>on</strong>ed factors varies am<strong>on</strong>g species. The<br />

s<str<strong>on</strong>g>of</str<strong>on</strong>g>twood species Salix spp. <str<strong>on</strong>g>and</str<strong>on</strong>g> Populus spp. tend to be better adapted to flooding than<br />

<strong>the</strong> hardwood broad leafed deciduous species Quercus spp, Ulmus spp. <str<strong>on</strong>g>and</str<strong>on</strong>g> Fraxinus<br />

spp. (Vreugdenhil et al. 2006). In Europe, this results in a typical z<strong>on</strong>ati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>the</strong><br />

s<str<strong>on</strong>g>of</str<strong>on</strong>g>twood species Salix spp. <str<strong>on</strong>g>and</str<strong>on</strong>g> Populus spp. near <strong>the</strong> main channel <str<strong>on</strong>g>and</str<strong>on</strong>g> <strong>the</strong> hardwood<br />

species Quercus spp., Ulmus spp. as well as Fraxinus spp. dominating <strong>the</strong> less<br />

frequently flooded sites (Ward et al. 2002; Ellenberg 1988). These observati<strong>on</strong>s could<br />

be affirmed within this study, though <strong>the</strong> s<str<strong>on</strong>g>of</str<strong>on</strong>g>twood z<strong>on</strong>e was <str<strong>on</strong>g>of</str<strong>on</strong>g>ten narrow <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

sometimes completely lacking, possibly due to already reduced river dynamics. Both<br />

poplar species were obviously restricted to bare soils in, or adjacent to <strong>the</strong> open riverbed<br />

where flood dynamic is greatest. Populus nigra prefers <strong>the</strong> upper sites (Fig. 5.3 , Fig.<br />

5.4 <str<strong>on</strong>g>and</str<strong>on</strong>g> Fig. 5.6), obviously better adapted to survive drier periods in summer. Glenz et<br />

al. (2006) indicate its flooding tolerance with high (4) (Table 5.1).<br />

-<str<strong>on</strong>g>Ecology</str<strong>on</strong>g> <str<strong>on</strong>g>and</str<strong>on</strong>g> <str<strong>on</strong>g>regenerati<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>forest</str<strong>on</strong>g> <str<strong>on</strong>g>communities</str<strong>on</strong>g> <strong>on</strong> <strong>the</strong> <strong>alluvial</strong> <strong>fan</strong> near Qakh (Northwestern Azerbaijan)-<br />

39

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