Nicola Arndt und Matthias Pohl - Neobiota

Nicola Arndt und Matthias Pohl - Neobiota Nicola Arndt und Matthias Pohl - Neobiota

22.02.2013 Aufrufe

ailway sidings. Figure 2: Coincidence map of the characteristic species of F8 Atlantic-Subatlantic birch-oak forest and its replacements in West Yorkshire. Over this diverse terrain, the mosaic of existing vegetation types looks complicated but the underlying pattern is fairly simple (RODWELL & DRING 2000). The major contrasts in the composition and distribution of the plant communities reflect spatial differences in acidity, trophic state and wetness of the soils and the progress of succession in the time since abandonment of the site. We can recognise three such successional systems and associated vegetation complexes. On the most acidic, nutrientpoor and driest soils, we can predict that the F8 Atlantic-Subatlantic birch-oak forest described above will be the eventual end point of succession. On the neutral, mesotrophic and moist soils, there will be F32 Irish-British-Norman oak-ash forests and, on the wet, eutrophic soils, U7 Irish-British alluvial forest with ash and alder. Using the UK National Vegetation Classification, we can characterise each of the earlier stages of vegetation within the complexes that are represented on the site and understand something of their ecological inter-relationships (Figure 3). With a wider knowledge of comparable sites where these complexes of replacement vegetation types are represented, we can envisage a greater diversity of plant communities within the successional dynamic of the map units than are present at Darwen Parkway now and specify the kinds of intervention necessary to develop and sustain each of these plant communities there (Figure 4). In this way, the Vegetation Map of Europe can help us visualise alternative future landscapes and manage the ecological processes. 374

Figure 3: Woodlands and their replacements at Darwen Parkway. Figure 4: A fuller diversity of potential vegetation types at Darwen Parkway. 375

ailway sidings.<br />

Figure 2: Coincidence map of the characteristic species of F8 Atlantic-Subatlantic birch-oak forest and its<br />

replacements in West Yorkshire.<br />

Over this diverse terrain, the mosaic of existing vegetation types looks complicated but the <strong>und</strong>erlying<br />

pattern is fairly simple (RODWELL & DRING 2000). The major contrasts in the composition and<br />

distribution of the plant communities reflect spatial differences in acidity, trophic state and wetness of<br />

the soils and the progress of succession in the time since abandonment of the site. We can recognise<br />

three such successional systems and associated vegetation complexes. On the most acidic, nutrientpoor<br />

and driest soils, we can predict that the F8 Atlantic-Subatlantic birch-oak forest described above<br />

will be the eventual end point of succession. On the neutral, mesotrophic and moist soils, there will be<br />

F32 Irish-British-Norman oak-ash forests and, on the wet, eutrophic soils, U7 Irish-British alluvial<br />

forest with ash and alder. Using the UK National Vegetation Classification, we can characterise each<br />

of the earlier stages of vegetation within the complexes that are represented on the site and <strong>und</strong>erstand<br />

something of their ecological inter-relationships (Figure 3).<br />

With a wider knowledge of comparable sites where these complexes of replacement vegetation types<br />

are represented, we can envisage a greater diversity of plant communities within the successional<br />

dynamic of the map units than are present at Darwen Parkway now and specify the kinds of<br />

intervention necessary to develop and sustain each of these plant communities there (Figure 4). In this<br />

way, the Vegetation Map of Europe can help us visualise alternative future landscapes and manage the<br />

ecological processes.<br />

374

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