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Understanding juvenile responses to habitat features during dispersal will aid in developing realistic, predictive models of amphibian movement that could be used to further conservation and management efforts such as mitigation and restoration, and will also add to theory about how movement mechanisms during dispersal impact population persistence in altered landscapes.
The Waratah is bird and mammal pollinated [ 13] and our data show that gene flow across large distances is possible (within the coastal group for example), thus suggesting that factors other than dispersal impact on between-population connectivity.
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It is unknown if or how animal mediated dispersal impacts aquatic hyphomycete population structure.
Additionally, we can draw several general insights about how dispersal impacts selection and evolution of Allee effects in an invasion context.
In our model, dispersal impacts survival ecologically through the critical patch size, and genetically, as individuals may move from areas where they are well adapted (i.e., the population density is greater than the Allee threshold or mean trait value) to sink regions, where they are maladapted.
The highly restricted geographical distribution of the genus is of great interest in terms of both abiotic (continental drift) and biotic (long-distance dispersal) impacts on monocot plant speciation events and their timing, and of evolutionary patterns of diversification leading to the extant taxa.
Costa, A. et al. Quantifying volcanic ash dispersal and impact of the Campanian Ignimbrite super-eruption.
Rare long distance dispersal events impact the demography and the genetic structure of populations.
First of all, when considered at village scale to minimize the spatial smoothing effects of mosquito dispersal upon impact, we see that reasonably high coverage is achieved in all villages and that between-village variation in EIR is at least equivalent to that which might be expected from such modest variations in coverage with nets of generally poor quality.
These results indicate that biofilm dispersal is impacted by the age of the biofilm as well as number of bacterial cells used to initiate biofilm growth, illustrating the fact that biofilms established using different conditions are distinct from each other.
The geographic range of S. pratensis is unknown and it is not possible to estimate rates of migration from our current sample size, or to estimate whether dispersal limitation impacts the biogeographic pattern of genetic diversity within the species at very large spatial scales (e.g. continental).
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