Nicola Arndt und Matthias Pohl - Neobiota
Nicola Arndt und Matthias Pohl - Neobiota Nicola Arndt und Matthias Pohl - Neobiota
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
- Seite 325 und 326: % Arten 80 70 60 50 40 30 20 10 0 A
- Seite 327 und 328: 2. ALPEN - ANGRENZENDE GEB. a) ALP-
- Seite 329 und 330: Tabelle 2: Verteilung der wichtigst
- Seite 331 und 332: % der Arten 70 60 50 40 30 20 10 0
- Seite 333 und 334: Literatur ADLER, W.; OSWALD K. & FI
- Seite 335 und 336: MEUSEL, H.; JÄGER, E.J. & WEINERT,
- Seite 337 und 338: Anwendung und Auswertung der Karte
- Seite 339 und 340: Abb. 1: Klimadiagramme ausgewählte
- Seite 341 und 342: (S. graeca, S. hajastana u. a.) und
- Seite 343 und 344: Die Kräuterfluren besiedeln vorwie
- Seite 345 und 346: Picea orientalis gehört zur Sektio
- Seite 347: Anschrift des Autors: Prof. Dr. Gio
- Seite 350 und 351: Tabellen mit Tausenden von Aufnahme
- Seite 352 und 353: Figure 1a/Figure 1b: The Dutch vers
- Seite 354 und 355: (2) Already in 1994, the computer p
- Seite 356 und 357: types, the computerized links betwe
- Seite 358 und 359: MUCINA, L.; RODWELL, J.S.; SCHAMIN
- Seite 361: Anwendung der Europakarte bei der W
- Seite 364 und 365: secondary in origin but include sta
- Seite 366 und 367: Table 2: Potential forest types occ
- Seite 368 und 369: available, in part for social reaso
- Seite 370 und 371: Table 3: Principal potential forest
- Seite 373 und 374: Application and Analysis of the Map
- Seite 375: Sometimes, where there is comprehen
- Seite 379 und 380: 25% 6% 0% 1% 2% 1% 4% 0% 19% 42% U7
- Seite 381: Darwen Parkway and Outwood projects
- Seite 385 und 386: Anwendung und Auswertung der Karte
- Seite 387 und 388: of natural oak regeneration (e.g.,
- Seite 389 und 390: Im vorliegenden Beitrag steht die V
- Seite 391 und 392: Abb. 1: Birken-Pionierwald mit eind
- Seite 393 und 394: Wollgras- Torfmoos-KI-Typ naß Torf
- Seite 395 und 396: (EI-)KI Hylocom.-Vaccin. KI Hylocom
- Seite 397 und 398: ausgewiesene ostdeutsche Gebiete we
- Seite 399 und 400: BOHN, U.; GOLLUB, G. & HETTWER, C.
- Seite 401 und 402: Application and Analysis of the Map
- Seite 403 und 404: possibility to apply geostatistical
- Seite 405 und 406: The mean sensitivity is a measure o
- Seite 407 und 408: Figure 8/9: Time series of radial i
- Seite 409 und 410: precepitation index precepitation (
- Seite 411: MATHERON, G. (1955): Application de
- Seite 414 und 415: and site conditions as well. In thi
- Seite 416 und 417: und grenzen sich von anderen Wald-
- Seite 418 und 419: Tabelle 1: Ausgewählte ökosystema
- Seite 420 und 421: 418 700 600 Perlgras- Buchenwald 50
- Seite 422 und 423: 420 Abb. 3: Natürliches Potential
- Seite 424 und 425: 83 % 86 % 96 % 100 km Abb. 4: Ökol
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