Summary1. Fragmentation and habitat loss affects both existing and introduced populations. Small habitat areas may have harsher biotic and abiotic conditions, as well as restricting population sizes. Loss of connectivity reduces the opportunities for individuals to move between patches to rescue populations or to re-colonize patches. Knowledge of how landscape composition affects the introduced populations is therefore essential for successful management and future re-introductions.
2.To study the effect of landscape composition and structure on the success of colonization, population growth and dispersal distances, we introduced Roesel's bushcrickets Metrioptera roeseli to 70 habitat islands in areas previously unoccupied by the species. The introduction sites differed in habitat area and connectivity. The population survival and dispersal were then studied for 5 years after initial introductions. 3. In addition to results showing the importance of suitable habitat for population persistence, connectivity in form of linear landscape elements and nodes was also crucial. Linear landscape elements and / or nodes were important for colonization success, growth and dispersal. Linear landscape elements and nodes also reduced the negative effects of unsuitable habitat (matrix) and isolation from suitable habitat and on the populations. 4. These results stress the importance of connectivity in the landscape for population survival and establishment. Consideration of this should be taken into account in both management and re-introductions of bush-crickets and other invertebrates with similar population characteristics and behaviour.
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Aim To examine temporal variation in nestedness and whether nestedness patterns predict colonization, extinction and turnover across islands and species.
Location Dahlak Archipelago, Red Sea.
Method The distributions of land birds on 17 islands were recorded in two periods 30 years apart. Species and islands were reordered in the Nestedness Temperature Calculator, software for assessing degrees of nestedness in communities. The occupancy probability of each cell, i.e. species–island combinations, was calculated in the nested matrix and an extinction curve (boundary line) was specified. We tested whether historical and current nested ranks of species and islands were correlated, whether there was a relationship between occupancy probability (based on the historical data) and number of extinctions or colonizations (regression analyses) and whether the boundary line could predict extinctions and colonizations (chi‐square analyses).
Results Historical and current nested ranks of islands and species were correlated but changes in occupancy patterns were common, particularly among bird species with intermediate incidence. Extinction and turnover of species were higher for small than large islands, and colonization was negatively related to isolation. As expected, colonizations were more frequent above than below the boundary line. Probability of extinction was highest at intermediate occupancy probability, giving a quadratic relationship between extinction and occupancy probability. Species turnover was related to the historical nested ranks of islands. Colonization was related negatively while extinction and occupancy turnover were related quadratically to historical nested ranks of species.
Main conclusions Some patterns of the temporal dynamics agreed with expectations from nested patterns. However, the accuracy of the predictions may be confounded by regional dynamics and distributions of idiosyncratic, resource‐limited species. It is therefore necessary to combine nestedness analysis with adequate knowledge of the causal factors and ecology of targeted species to gain insight into the temporal dynamics of assemblages and for nestedness analyses to be helpful in conservation planning.
Many species of temperate-zone passerines show a pronounced daily cycle in body mass. Energy reserves are built up during the day and consumed the following night. The size of reserves is often viewed as a compromise between the risk of starvation and the cost of carrying an excessive fat load. This trade-off calls for state-dependent foraging behaviour, where current reserves and time of day are two crucial factors. The foraging strategy of the birds may then be reflected by the pattern of daily mass gain rate. We temporarily increased energy expenditure in captive great tits (Parus major) by experimentally lowering the overnight temperature. The birds' response to the treatment was to rapidly compensate for reduced morning reserves. Such an increased rate of mass gain suggests state-dependent foraging, and that some feeding opportunities are normally rejected. The rate of return to the normal pattern of fat accumulation suggests that in these birds, foraging is not constrained by physiological limitations.
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