Abstracts available here - Society for Conservation Biology
Abstracts available here - Society for Conservation Biology
Abstracts available here - Society for Conservation Biology
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25th International Congress <strong>for</strong> <strong>Conservation</strong> <strong>Biology</strong> • Auckland, New Zealand • 5-9 December 2011<br />
2011-12-08 10:30 Climate change, Variability and conservation<br />
impacts in Australia<br />
Prowse, TAA, University of Adelaide; Brook, BW*, University of<br />
Adelaide;<br />
Australian conservation scientists, managers and decision makers must<br />
come to grips with anthropogenic climate change, imposed upon an already<br />
variable regional climate system. Pre- and post-instrumental records and<br />
climate proxies indicate that Australia has experienced wet and dry cycles<br />
over intra-decadal to millennial time scales. Precipitation variation across<br />
Australia is correlated with different climate features but reliable tools <strong>for</strong><br />
seasonal rainfall prediction are still some years away. Atmosp<strong>here</strong>-Ocean<br />
General Circulation Models predict a widening of the Hadley circulation<br />
and strengthening of the Southern Annular Mode, which should result in<br />
reduced cool season rainfall over southern Australia. Shifts in the Australian<br />
climate over the Holocene epoch, most notably increased ENSO variability<br />
after 5 000 years ago, are associated with substantial vegetation change and<br />
indicate the speed at which ecosystems may be altered. The CO2 fertilization<br />
of plant biomes may mitigate increasing aridity to some extent but, in<br />
general, climate change is expected to negatively affect native vegetation<br />
and agricultural productivity. Sea-level rise is predicted to be substantial<br />
over this century and, when coupled with increased storm intensity, poses<br />
threats in the <strong>for</strong>m of erosion, salinization and flooding. The best chance<br />
of building adaptable ecosystems and preserving ecosystem services requires<br />
the extension, integration and possibly optimization of reserve systems, in<br />
concert with improved management of other threatening processes (habitat<br />
loss, invasive species, overexploitation, pollution and disease). In addition,<br />
a price on carbon dioxide emissions would provide incentives <strong>for</strong> privately<br />
funded re<strong>for</strong>estation schemes, but additional incentives promoting mixed<br />
species over monoculture plantings would be required to assure maximum<br />
biodiversity benefits.<br />
2011-12-09 11:00 <strong>Conservation</strong> Management of Complex Edge Effects<br />
Pryke, J. S.*, Stellenbosch University; Samways, M.J., Stellenbosch<br />
University;<br />
Understanding edge effects between trans<strong>for</strong>med landscapes and<br />
conservation areas is critical to conservation planning. As conservation<br />
areas in landscape mosaics are often composed of linear corridors, t<strong>here</strong><br />
are more edges than would occur naturally. To determine minimum<br />
width of corridors, we would first need to determine the extent of edge<br />
effects. Plantation <strong>for</strong>estry has trans<strong>for</strong>med much of the South African<br />
grasslands, with ecological networks (ENs) currently being used to mitigate<br />
this biodiversity loss and to maintain ecosystem processes. We compare<br />
arthropod biodiversity along transects that ran from within plantation<br />
blocks or indigenous <strong>for</strong>est patches (as a natural reference) into indigenous<br />
grassland corridors. Two types of exotic commercial trees and various tree<br />
age classes were studied. We found a 32 m edge zone from plantation blocks<br />
into grassland corridors. Few significant edge effects from plantation blocks<br />
occurred at greater distances than this, suggesting that grassland corridors<br />
with a width