24 research outputs found

    Speciation

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    The restoration of parasites, parasitoids and pathogens to heathland communities

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    Higher trophic level species such as parasites, parasitoids, and pathogens are frequently ignored in community studies, despite playing key roles in the structure, function, and stability of ecological communities. Furthermore, such species are typically among the last in a community to reestablish due to their reliance upon lower trophic level resources and a requirement for persistent, stable ecological conditions. Consequently their presence alone can be indicative of healthy ecosystems. Using replicated, quantitative food webs we studied the impacts of a restoration treatment upon the interactions of a tri-trophic community consisting of plants, their bumble bee pollinators, and the parasites, parasitoids, and pathogens of the bumble bees at heathland sites. We found the lower trophic levels of the community successfully reinstated at restored relative to control sites. However the abundance, load per host, prevalence of parasitism, prevalence of superparasitism, and host range of a key dipteran parasitoid of the family Conopidae were all significantly reduced in restored heathlands. Potential causes for this incomplete reestablishment at restored sites include the lag in floral resources due to differences in floral species composition, and the reduced ability of this parasitoid species in accessing host resources relative to other natural enemy species present in these communities. Moreover the incomplete reinstatement of the natural enemy community was found to significantly reduce levels of network vulnerability (a measure of how vulnerable prey is to being consumed) at restored sites relative to ancient, control network

    Global warming and the disruption of plant-pollinator interactions

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    Anthropogenic climate change is widely expected to drive species extinct by hampering individual survival and reproduction, by reducing the amount and accessibility of suitable habitat, or by eliminating other organisms that are essential to the species in question. Less well appreciated is the likelihood that climate change will directly disrupt or eliminate mutually beneficial (mutualistic) ecological interactions between species even before extinctions occur. We explored the potential disruption of a ubiquitous mutualistic interaction of terrestrial habitats, that between plants and their animal pollinators, via climate change. We used a highly resolved empirical network of interactions between 1420 pollinator and 429 plant species to simulate consequences of the phenological shifts that can be expected with a doubling of atmospheric CO2. Depending on model assumptions, phenological shifts reduced the floral resources available to 1750% of all pollinator species, causing as much as half of the ancestral activity period of the animals to fall at times when no food plants were available. Reduced overlap between plants and pollinators also decreased diet breadth of the pollinators. The predicted result of these disruptions is the extinction of pollinators, plants and their crucial interactions

    Differences in physiological tolerance between co-existing taxa of the Madeiran land snail genus Heterostoma measured under controlled humidity and rainfall

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    The Madeiran land snail genus Heterostoma contains two taxa distinguished by differences in genital anatomy: one has full hermaphroditic genitalia (euphallic) while the other lacks the distal male organs (hemiphallic). Snails from the Madeiran islands of Porto Santo and Ilheu de Cima were kept under controlled conditions differing in humidity and simulated rainfall. There were four treatments: (1) low humidity, no rainfall; (2) low humidity, rainfall; (3) high humidity, no rainfall; (4) high humidity, rainfall. For snails from Porto Santo there were viability differences between taxa under all treatments such that hemiphallics were most viable under treatment 1 and euphallics were more viable under all other treatments. There were no signicant differences between taxa taken from Ilheu de Cima. This may be a real effect or the result of smaller sample size or a combination of both. Under all conditions, both taxa from both islands show a time-dependent reduction in viability in response to rainfall. Taxa from Porto Santo also respond differently to humidity with hemiphallics surviving for less time than euphallics at high humidity. These results are interpreted as showing a difference in physiological tolerance between taxa from Porto Santo with respect to humidity. It is suggested that this ecological difference may have been a factor in the divergence of the taxa, perhaps through interaction with genital anatomy variation. No rm conclusions can yet be drawn regarding samples taken from Ilheu de Cima
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