Article:
Theurillat, J.P., Felber, F., Geissler, P., Gobat, J.-M., Fierz, M.,
Fischlin, A., Kuepfer, P., Schluessel, A., Velluti, C., Zhao, G.-F. &
Williams, J., 1998. Sensitivity of plant and soil ecosystems of the Alps
to climate change. In: Cebon, P., Dahinden, U., Davies, H.C., Imboden,
D.M. & Jaeger, C.C. (eds.), Views from the Alps: regional perspectives
on climate change. MIT Press, Boston, Massachusetts a.o., pp. 289-308.
Abstract:
In highly structured vegetation, synusiae of the understory are unlikely to
react directly to climate change but rather only indirectly to a change in their
microhabitat conditions.
Present climatic climax plant communities are likely to persist in climate
change as edaphic climaxes.
Present edaphic climaxes are likely to persist temporally and spatially in
climate change according to their buffering capacities, that is, so far as their
limiting factors are not changed.
Natural landscape is likely to change at a differential rate, according to its
component elements (lagging vs. rapid change).
The cultural landscape that will undergo climate change may be very different
from today's.
The response of species, plant communities and landscape to a temperature
increase is not likely to be linear, and there may be an inertia of 1-2 K.
A temperature increase of 3-4 K would very likely have a profound effect
at every level of complexity, since it equals the temperature amplitude of an
entire vegetation belt.
Fragmentation, diminution of populations, and selective extinctions of
high alpine and arctic stenoicious relict plant populations of bryophytes and
vascular plants are likely over the entire Alps if the temperature increases by
3-4 K.
Alpine endemics restricted to tops of low mountains (i.ee., those lacking
nival belts, mainly in the eastern Alps) are likely to be severely endangered
of disappearance/extinction if the temperature increases by 3-4 K.
Phenotypic plasticity and genetic adaptation might buffer the effect of climatic
change in some cases for vascular plants, and perhaps more frequently
for bryophytes.
Changes in forest types might occur in 30-55 percent of the forested area
for an increase of 1-1.4 K, and in up to 55-89 percent for a 2-2.8 K
increase, according to static modeling of Swiss forests (Kienast, Brzeziecki,
and Wildi 1995, 1996).
Adaptation of forests and tree species to climate change cannot be suitably
established without taking into account the typically high genetic diversity
of tree populations and the maintainance of that diversity.
For an increase of 1-2 K in the mean annual temperature, the present
upper subalpine forest limit is not likely to shift upward much more than
100-200 meters, because of its temperature-related inertia, but the kamp[zone
might move into the low alpine belt in favorable places.
For an increase of 3-4 K in the mean annual temperature, the kamp[zone
would be very likely to invade the alpine belt, with an upward shift of the
forest limit into the low alpine belt.
With an increase of 3-4 K in the mean annual temperature, subalpine elements
would be likely to invade the entire alpine vegetation belt, and new
plant communities would be likely to replace in part the present communities.
For an increase of 1-2 K in the mean annual temperature, human use might
slow down the subalpine vegetation's upward shift, in particular that of
heaths, shrubs, and trees, through an intensification of pasturing. In contrast,
humans could also accelerate the shift through abandoning agricultural
activities and afforestion of the upper subalpine belt.
The upward shift of the present alpine vegetation into the nival belt,
where it exists, might epend more on edaphic factors than on climatic onces
because of the upper alpine and nival belts increasing steepness.
Therefore, it is likely that present alpine plant communities on gentle
slopes would disappear.
Carbonate soils would likely be less prone to react to climate change than
noncarbonate soils, thus acting nonsynergistically on vegetation change.
Processes in soils operate at different rates, and many happen on the timescale
of one year or tens of years. The accepted idea that soils evolve on a
scale of centuries or millenia must be abandoned in considerations of climate
change.
Organic matter in soils is the key factor that would be affected, directly or
indirectly, qualitatively and quantitatively, by climate change, but its evolution
cannot be dissociated from that of soil nitrogen content.
Nitrogen content, form, and cycle would be affected, and cannot be dissociated
from changes in organic matter, as, for example, an increase in
humification.
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