Nicola Arndt und Matthias Pohl - Neobiota
Nicola Arndt und Matthias Pohl - Neobiota Nicola Arndt und Matthias Pohl - Neobiota
3.4 Comparison of time series As illustrated in Figure 7, Norway spruce exhibits lower sensitivity on sites within its natural range than on sites outside this range. To examine simultaneously the temporal behaviour of the annual radial increment, time series of radial increment indices are represented (Figure 8 and 9). For the index values, the time series of the annual radial increment are detrended and standardized to a mean of 100 %. The radial increment indices of Norway spruce growing on sites within their natural distributional range are compared with those from trees growing on sites in the main formation of “oak hornbeam forests” where the largest mean sensitivity was observed (Figure 5). Despite distinct differences in baseline climatic (Table 1) and geological conditions between the sites in these two areas, the radial growth reactions are similar. In both cases local minima can be observed in the years 1948, 1962, and the absolute minimum value in both cases occurs in 1976. Synchronous maxima occur in the years 1955 and 1982. However the degree of variability is different: a large amount of variability can be observed in the areas where spruce grows outside its distributional range on sites naturally dominated by oak-hornbeam forests. The year-to-year behaviour of radial growth is more complacent on sites within its natural range. In Figures 10 time series of radial growth indices are compared with time series of growing season precipitation. Again we have calculated the values for Norway spruce growing on sites in the main forest formations “montane spruce and fir forests” and “oak-hornbeam forests”. When comparing the time series of the mean radial increment indices it is evident that spruce growing on sites outside its distributional range shows larger growth variations. The central figure shows the precipitation index, which is the percentage-deviation of the precipitation from the long-term mean (1961-90). The courses of the time series are in both cases similar: extraordinarily dry conditions (e.g. 1947, 1949, 1976) as well as above average moist conditions occurred in both areas in the same years 406 growth index 160 140 120 100 80 60 40 1941 1943 1945 1947 1949 1951 1953 1955 1957 1959 1961 1963 1965 1967 1969 oak hornbeam forests spruce and fir forests 1971 1973 1975 1977 1979 1981 1983
precepitation index precepitation (mm) 160 140 120 100 80 60 40 800 700 600 500 400 300 200 100 0 1941 1941 1943 1943 1945 1945 1947 1947 1949 1949 1951 1951 1953 1953 1955 1955 1957 1957 1959 1959 Figure 10: Time series of radial growth indices (%, top), precipitation index (%, centre) and absolute precipitation sum (mm, below) during the growing season (May-September) on Norway spruce sites within their natural distributional range (light grey line) and in the area with a natural potential vegetation of mixed oak-hornbeam forests (black thin line). with similar amplitudes. When looking on the absolute precipitation values it can be seen that the sites in the areas of oak-hornbeam forests received significantly lower precipitation than in the area naturally dominated by Norway spruce. During drought periods, spruce reaches the critical point of soil moisture depletion earlier and growth decreases more strongly. However, spruce in the oak- 1961 1961 1963 year 1963 ye ar 1965 1965 1967 1967 1969 1969 1971 1971 1973 1973 1975 1975 1977 1977 1979 1979 1981 1981 1983 1983 407
- 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 und 376: Sometimes, where there is comprehen
- Seite 377 und 378: Figure 3: Woodlands and their repla
- 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: Figure 8/9: Time series of radial i
- 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
- Seite 426 und 427: 424 Abb. 5: Natürliches Potential
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- Seite 430 und 431: SCHIKORA, K. et al. (1981): Waldfl
- Seite 432 und 433: and tidal flat horizons on the East
- Seite 434 und 435: 1700 und 300 v. Chr. an. Eine letzt
- Seite 436 und 437: Ansteigen des Nordseespiegels um ca
- Seite 438 und 439: Anschrift des Autors: PD Dr. Holger
- Seite 440 und 441: Abb. 3: Unbedeichte Salzwiese im Ho
- Seite 442 und 443: 1 Einleitung Das Verbreitungsgebiet
- Seite 444 und 445: gesehen zeichnet sich der starke Er
- Seite 446 und 447: 6 Anwendung (und Auswertung) der Ka
- Seite 448 und 449: abnehmen, während thermophile Arte
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- Seite 452 und 453: Der Verdacht, daß die Klimaänderu
- Seite 454: WALTHER, G.-R. (2001a): Adapted beh
3.4 Comparison of time series<br />
As illustrated in Figure 7, Norway spruce exhibits lower sensitivity on sites within its natural range<br />
than on sites outside this range. To examine simultaneously the temporal behaviour of the annual<br />
radial increment, time series of radial increment indices are represented (Figure 8 and 9). For the index<br />
values, the time series of the annual radial increment are detrended and standardized to a mean of<br />
100 %. The radial increment indices of Norway spruce growing on sites within their natural<br />
distributional range are compared with those from trees growing on sites in the main formation of “oak<br />
hornbeam forests” where the largest mean sensitivity was observed (Figure 5).<br />
Despite distinct differences in baseline climatic (Table 1) and geological conditions between the sites<br />
in these two areas, the radial growth reactions are similar. In both cases local minima can be observed<br />
in the years 1948, 1962, and the absolute minimum value in both cases occurs in 1976. Synchronous<br />
maxima occur in the years 1955 and 1982. However the degree of variability is different: a large<br />
amount of variability can be observed in the areas where spruce grows outside its distributional range<br />
on sites naturally dominated by oak-hornbeam forests. The year-to-year behaviour of radial growth is<br />
more complacent on sites within its natural range.<br />
In Figures 10 time series of radial growth indices are compared with time series of growing season<br />
precipitation. Again we have calculated the values for Norway spruce growing on sites in the main<br />
forest formations “montane spruce and fir forests” and “oak-hornbeam forests”.<br />
When comparing the time series of the mean radial increment indices it is evident that spruce growing<br />
on sites outside its distributional range shows larger growth variations. The central figure shows the<br />
precipitation index, which is the percentage-deviation of the precipitation from the long-term mean<br />
(1961-90). The courses of the time series are in both cases similar: extraordinarily dry conditions (e.g.<br />
1947, 1949, 1976) as well as above average moist conditions occurred in both areas in the same years<br />
406<br />
growth index<br />
160<br />
140<br />
120<br />
100<br />
80<br />
60<br />
40<br />
1941<br />
1943<br />
1945<br />
1947<br />
1949<br />
1951<br />
1953<br />
1955<br />
1957<br />
1959<br />
1961<br />
1963<br />
1965<br />
1967<br />
1969<br />
oak hornbeam forests<br />
spruce and fir forests<br />
1971<br />
1973<br />
1975<br />
1977<br />
1979<br />
1981<br />
1983