Global Change Abstracts The Swiss Contribution - SCNAT
Global Change Abstracts The Swiss Contribution - SCNAT
Global Change Abstracts The Swiss Contribution - SCNAT
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<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 71<br />
lichens by assessing species diversity and cover<br />
of lichens in climbed and unclimbed areas of 10<br />
isolated cliffs in the northern <strong>Swiss</strong> Jura Mountains.<br />
We also investigated possible associations<br />
between lichens and lichen-feeding land snails on<br />
these cliffs. A total of 38 calcicolous lichen species,<br />
three bryophytes and one alga were found on<br />
the rock faces of 10 cliffs. Twenty lichen species<br />
(52.6%) were epilithic, 16(42.1%) endolithic and<br />
two (5.3%) foliose. Overall, the epilithic lichen species<br />
covered 8.3% of the rock surface, endolithic<br />
species 10.2%, and foliose species 0.03%. Climbed<br />
and unclimbed rock areas did not differ in total<br />
number of lichen species, species density (number<br />
of species per 100 cm(2)) or total lichen cover. However,<br />
the frequency of occurrence of epilithic lichens<br />
was lower along climbing routes than in unclimbed<br />
areas. A multi-response permutation test<br />
showed that the lichen community composition<br />
of climbed areas differed from that of unclimbed<br />
areas. <strong>The</strong> dissimilarity of lichen communities<br />
between climbed and unclimbed areas increased<br />
with increasing climbing intensity on the focal<br />
route in climbed areas, but not with the age of the<br />
climbing route. Five of the 11 snail species recorded<br />
on the cliff faces were specialized lichen feeders.<br />
Plots along climbing routes harboured fewer<br />
snail species than plots in unclimbed areas. Total<br />
snail abundance was positively correlated with lichen<br />
species richness, but no correlation between<br />
snail species richness and lichen species richness<br />
was found. Our results indicate that frequent rock<br />
climbing can change the lichen community and<br />
reduce the snail community of limestone cliffs.<br />
A climbing-related reduction of snail abundance<br />
may also alter the lichen-herbivore interaction<br />
and indirectly change competitive interactions<br />
among lichen species.<br />
Nova Hedwigia, 2007, V85, N3-4, NOV, pp<br />
429-444.<br />
08.1-90<br />
Evaluating macrolichens and environmental<br />
variables as predictors of the diversity of epiphytic<br />
microlichens<br />
Bergamini A, Stofer S, Bolliger J, Scheidegger C<br />
Switzerland<br />
Biodiversity , Ecology , Forestry , Plant Sciences<br />
In contrast to the frequently assessed macrolichens,<br />
microlichens are rarely considered in biodiversity<br />
assessments despite their high species<br />
richness. Microlichens require generally a higher<br />
species identification effort than macrolichens.<br />
Thus, microlichens are more expensive to assess.<br />
Here we evaluate if macrolichen richness can be<br />
used as an indicator of total and threatened mi-<br />
crolichen richness. Furthermore, we tested if different<br />
sets of environmental variables (modelled<br />
climatic variables, forest structure, altitude, etc.)<br />
improve the regression models based on macrolichens<br />
only or even replace the macrolichens as<br />
predictors. Multiple linear regressions were used<br />
to model species richness of microlichens, and<br />
Poisson regressions for threatened microlichens.<br />
On 237 forest plots (200 m(2)) distributed randomly<br />
across Switzerland, 77 macrolichens and 219<br />
microlichens occurred. Macrolichen richness was<br />
positively related to the richness of microlichens.d.<br />
= 0-27) and, in combination with threatened macrolichens<br />
as an additional predictor, also to the<br />
number of threatened microlichens (R-dev(2) =<br />
0.14). Environmental variables alone and in different<br />
combinations explained between 0.20 and<br />
0.41 (R-adj.(2)) of the total variation of microlichen<br />
richness, and between 0.09 and 0.29 (R-dev.(2)) of<br />
the total variation of threatened microlichen<br />
richness. All models based on environmental variables<br />
were considerably improved when macrolichens<br />
were included. Furthermore, macrolichen<br />
richness turned out to be the most important variable<br />
in explaining species richness of all, as well<br />
as threatened microlichens. <strong>The</strong> best models for<br />
total microlichen richness reached a R-2 of 0.56.<br />
Threatened microlichens were more difficult to<br />
model with the best model reaching a R-dev.(2) of<br />
0.29. We conclude that in biodiversity assessments<br />
with scarce resources, lichen sampling could be<br />
focused on the better known macrolichens, at<br />
least in many temperate lowland and mountain<br />
forests. In combination with environmental variables,<br />
reliable predictions of microlichen richness<br />
can be expected. If the focus is on threatened microlichens,<br />
however, models were not reliable and<br />
specialized taxonomists are necessary to assess<br />
these species in the field.<br />
Lichenologist, 2007, V39, 5, pp 475-489.<br />
08.1-91<br />
Which species will succesfully track climate<br />
change? <strong>The</strong> influence of intraspecific competition<br />
and density dependent dispersal on<br />
range shifting dynamics<br />
Best A S, Johst K, Münkemüller T, Travis J M J<br />
Germany, Switzerland, Scotland<br />
Modelling , Meteorology & Atmospheric Sciences ,<br />
Ecology , Biodiversity<br />
Understanding the ability of species to shift their<br />
geographic range is of considerable importance<br />
given the current period of rapid climate change.<br />
Furthermore, a greater understanding of the spatial<br />
population dynamics underlying range shifting<br />
is required to complement the advances made