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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

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