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xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">March 2012</prism:coverDisplayDate><prism:volume xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">81</prism:volume><prism:number xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">2</prism:number><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">307</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">511</prism:endingPage><image rdf:resource="http://onlinelibrary.wiley.com/store/10.1111/jane.2012.81.issue-2/asset/cover.gif?v=1&amp;s=9b26f355616b6c9e9221f3c1e0d0b7e00e2e3d4b"/><items><rdf:Seq><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01949.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01956.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01965.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01964.x"/><rdf:li 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webs</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01949.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Bottom-up effects of species diversity on the functioning and stability of food webs</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Anita Narwani</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Asit Mazumder</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-10T19:25:44.594898-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01949.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01949.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01949.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> The importance of species diversity for the stability of populations, communities and ecosystem functions is a central question in ecology.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Biodiversity experiments have shown that diversity can impact both the average and variability of stocks and rates at these levels of ecological organization in single trophic-level ecosystems. Whether these impacts hold in food webs and across trophic levels is still unclear.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We asked whether resource species diversity, community composition and consumer feeding selectivity in planktonic food webs impact the stability of resource or consumer populations, community biomass and ecosystem functions. We also tested the relative importance of resource diversity and community composition.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We found that resource diversity negatively affected resource population stability, but had no effect on consumer population stability, regardless of the consumer’s feeding selectivity. Resource diversity had positive effects on most ecosystem functions and their stability, including primary production, resource biomass and particulate carbon, nitrogen and phosphorus concentrations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Community composition, however, generally explained more variance in population, community and ecosystem properties than species diversity <em>per se</em>. This result points to the importance of the outcomes of particular species interactions and individual species’ effect traits in determining food web properties and stability.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Among the stabilizing mechanisms tested, an increase in the average resource community biomass with increasing resource diversity had the greatest positive impact on stability.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> Our results indicate that resource diversity and composition are generally important for the functioning and stability of whole food webs, but do not have straightforward impacts on consumer populations.</p></div>]]></content:encoded><description>1. The importance of species diversity for the stability of populations, communities and ecosystem functions is a central question in ecology.2. Biodiversity experiments have shown that diversity can impact both the average and variability of stocks and rates at these levels of ecological organization in single trophic-level ecosystems. Whether these impacts hold in food webs and across trophic levels is still unclear.3. We asked whether resource species diversity, community composition and consumer feeding selectivity in planktonic food webs impact the stability of resource or consumer populations, community biomass and ecosystem functions. We also tested the relative importance of resource diversity and community composition.4. We found that resource diversity negatively affected resource population stability, but had no effect on consumer population stability, regardless of the consumer’s feeding selectivity. Resource diversity had positive effects on most ecosystem functions and their stability, including primary production, resource biomass and particulate carbon, nitrogen and phosphorus concentrations.5. Community composition, however, generally explained more variance in population, community and ecosystem properties than species diversity per se. This result points to the importance of the outcomes of particular species interactions and individual species’ effect traits in determining food web properties and stability.6. Among the stabilizing mechanisms tested, an increase in the average resource community biomass with increasing resource diversity had the greatest positive impact on stability.7. Our results indicate that resource diversity and composition are generally important for the functioning and stability of whole food webs, but do not have straightforward impacts on consumer populations.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01956.x" xmlns="http://purl.org/rss/1.0/"><title>Spatio-temporal patterns of habitat use in voles and shrews modified by density, season and predators</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01956.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Spatio-temporal patterns of habitat use in voles and shrews modified by density, season and predators</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Janne Sundell</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christina Church</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Otso Ovaskainen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-10T19:21:09.379023-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01956.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01956.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01956.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Although the intrinsic habitat preferences of a species can be considered to be fixed, the realized habitat use depends on the prevailing abiotic and biotic conditions. Often the core habitats are occupied by dense and stable populations, while marginal habitats become occupied only at times of high density. In a community of interacting species, habitat uses of different species become inter-related, for example an increased density of a strong competitor forcing a weaker competitor to use more marginal habitats.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We studied the spatio-temporal distribution patterns of three common small mammal species, the bank vole <em>Myodes glareolus</em>; the field vole <em>Microtus agrestis</em>; and the common shrew <em>Sorex araneus</em>, in a 4-year trapping study carried out on six large islands, each containing a mixture of three main habitat types (forest, field and clear-cut). We experimentally released least weasels (<em>Mustela n. nivalis</em>) to some of the islands to see how the focal species respond to increased predation pressure.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Both vole species were largely restricted to their core habitats (bank voles to forests and field voles to fields) at times of low population density. With increasing density, the relative habitat use of both species increased in the clear-cut areas. The common shrew was a generalist in its habitat use at all population densities.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> The release of the weasels changed the habitat use of all study species.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> The vole species showed a stronger aggregated pattern than the common shrew, especially at low population density. The vole aggregations remained in the same localities between seasons, except in the case of bank voles after the weasels were released.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Bank voles and field voles avoided each other at high density.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> We conclude that intrinsically differential habitat requirements and flexibility to modify habitat use facilitate the coexistence of the two competing vole species in mosaic landscapes consisting of boreal forests and open habitats.</p></div>]]></content:encoded><description>1. Although the intrinsic habitat preferences of a species can be considered to be fixed, the realized habitat use depends on the prevailing abiotic and biotic conditions. Often the core habitats are occupied by dense and stable populations, while marginal habitats become occupied only at times of high density. In a community of interacting species, habitat uses of different species become inter-related, for example an increased density of a strong competitor forcing a weaker competitor to use more marginal habitats.2. We studied the spatio-temporal distribution patterns of three common small mammal species, the bank vole Myodes glareolus; the field vole Microtus agrestis; and the common shrew Sorex araneus, in a 4-year trapping study carried out on six large islands, each containing a mixture of three main habitat types (forest, field and clear-cut). We experimentally released least weasels (Mustela n. nivalis) to some of the islands to see how the focal species respond to increased predation pressure.3. Both vole species were largely restricted to their core habitats (bank voles to forests and field voles to fields) at times of low population density. With increasing density, the relative habitat use of both species increased in the clear-cut areas. The common shrew was a generalist in its habitat use at all population densities.4. The release of the weasels changed the habitat use of all study species.5. The vole species showed a stronger aggregated pattern than the common shrew, especially at low population density. The vole aggregations remained in the same localities between seasons, except in the case of bank voles after the weasels were released.6. Bank voles and field voles avoided each other at high density.7. We conclude that intrinsically differential habitat requirements and flexibility to modify habitat use facilitate the coexistence of the two competing vole species in mosaic landscapes consisting of boreal forests and open habitats.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01965.x" xmlns="http://purl.org/rss/1.0/"><title>Intraspecific trait cospecialization of constitutive and inducible morphological defences in a marine snail from habitats with different predation risk</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01965.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Intraspecific trait cospecialization of constitutive and inducible morphological defences in a marine snail from habitats with different predation risk</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paul E. Bourdeau</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-09T19:38:17.446243-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01965.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01965.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01965.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Studies examining the integration of constitutive and inducible aspects of multivariate defensive phenotypes are rare.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> I asked whether marine snails (<em>Nucella lamellosa</em>) from habitats with and without abundant predatory crabs differed in constitutive and inducible aspects of defensive shell morphology.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> I examined multivariate shell shape development of snails from each habitat in the presence and absence of waterborne cues from feeding crabs (<em>Cancer productus</em>). I also examined the influence of constitutive and inducible shell morphology on resistance to crushing.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Regardless of the presence of crabs, snails from high-risk (HR) habitats developed rotund, short-spired shells, while snails from low-risk habitats developed elongate shells, tall-spired shells, indicating among-habitat divergence in constitutive shell shape. Moreover, allometry analyses indicated that constitutive developmental patterns underlying this variation also differed between habitats. However, snails from HR habitats showed greater plasticity for apertural lip thickness and apertural area in the presence of crab cues, indicating among-habitat variation in defence inducibility.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Both shell shape and apertural lip thickness contributed to shell strength suggesting that constitutive shell shape development and inducible lip thickening have evolved jointly to form an effective defence in habitats where predation risk is high.</p></div>]]></content:encoded><description>1. Studies examining the integration of constitutive and inducible aspects of multivariate defensive phenotypes are rare.2. I asked whether marine snails (Nucella lamellosa) from habitats with and without abundant predatory crabs differed in constitutive and inducible aspects of defensive shell morphology.3. I examined multivariate shell shape development of snails from each habitat in the presence and absence of waterborne cues from feeding crabs (Cancer productus). I also examined the influence of constitutive and inducible shell morphology on resistance to crushing.4. Regardless of the presence of crabs, snails from high-risk (HR) habitats developed rotund, short-spired shells, while snails from low-risk habitats developed elongate shells, tall-spired shells, indicating among-habitat divergence in constitutive shell shape. Moreover, allometry analyses indicated that constitutive developmental patterns underlying this variation also differed between habitats. However, snails from HR habitats showed greater plasticity for apertural lip thickness and apertural area in the presence of crab cues, indicating among-habitat variation in defence inducibility.5. Both shell shape and apertural lip thickness contributed to shell strength suggesting that constitutive shell shape development and inducible lip thickening have evolved jointly to form an effective defence in habitats where predation risk is high.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01964.x" xmlns="http://purl.org/rss/1.0/"><title>Life histories have a history: effects of past and present conditions on adult somatic growth rates in wild Trinidadian guppies</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01964.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Life histories have a history: effects of past and present conditions on adult somatic growth rates in wild Trinidadian guppies</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sonya K. Auer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Andrés Lopez-Sepulcre</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas Heatherly</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tyler J. Kohler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ronald D. Bassar</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Steven A. Thomas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David N. Reznick</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-09T19:36:19.939779-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01964.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01964.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01964.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Environmental conditions in the present, more recent past and during the juvenile stage can have significant effects on adult performance and population dynamics, but their relative importance and potential interactions remain unexplored.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We examined the influence of food availability at the time of sampling, 2 months prior and during the juvenile stage on adult somatic growth rates in wild Trinidadian guppies (<em>Poecilia reticulata</em>).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We found that food availability during both the early and later parts of an individual’s ontogeny had important consequences for adult growth strategies, but the direction of these effects differed among life stages and their magnitude, in some cases, depended on food levels experienced during other life stages. Current food levels and those 2 months prior to growth measurements had positive effects on adult growth rate; though, food levels 2 months prior had a greater effect on growth than current food levels. In contrast, the effects of food availability during the juvenile stage were higher in magnitude but opposite in direction to current food levels and those 2 months prior to growth rate measurements. Individuals recruiting under low food levels grew faster as adults than individuals recruiting during periods of high food availability. There was also a positive interaction between food levels experienced during the juvenile stage and 2 months prior such that the effects of juvenile food level diminished as the food level experienced 2 months prior increased.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> These results suggest that the similar conditions occurring at different life stages can have different effects on short- and long-term growth strategies of individuals within a population. They also demonstrate that, while juvenile conditions can have lasting effects on adult performance, the strength of that effect can be dampened by environmental conditions experienced as an adult.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> A simultaneous consideration of past events in both the adult and juvenile stage may therefore improve predictions for individual- and population-level responses to environmental change.</p></div>]]></content:encoded><description>1. Environmental conditions in the present, more recent past and during the juvenile stage can have significant effects on adult performance and population dynamics, but their relative importance and potential interactions remain unexplored.2. We examined the influence of food availability at the time of sampling, 2 months prior and during the juvenile stage on adult somatic growth rates in wild Trinidadian guppies (Poecilia reticulata).3. We found that food availability during both the early and later parts of an individual’s ontogeny had important consequences for adult growth strategies, but the direction of these effects differed among life stages and their magnitude, in some cases, depended on food levels experienced during other life stages. Current food levels and those 2 months prior to growth measurements had positive effects on adult growth rate; though, food levels 2 months prior had a greater effect on growth than current food levels. In contrast, the effects of food availability during the juvenile stage were higher in magnitude but opposite in direction to current food levels and those 2 months prior to growth rate measurements. Individuals recruiting under low food levels grew faster as adults than individuals recruiting during periods of high food availability. There was also a positive interaction between food levels experienced during the juvenile stage and 2 months prior such that the effects of juvenile food level diminished as the food level experienced 2 months prior increased.4. These results suggest that the similar conditions occurring at different life stages can have different effects on short- and long-term growth strategies of individuals within a population. They also demonstrate that, while juvenile conditions can have lasting effects on adult performance, the strength of that effect can be dampened by environmental conditions experienced as an adult.5. A simultaneous consideration of past events in both the adult and juvenile stage may therefore improve predictions for individual- and population-level responses to environmental change.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01963.x" xmlns="http://purl.org/rss/1.0/"><title>Estimating Brownian motion dispersal rate, longevity and population density from spatially explicit mark–recapture data on tropical butterflies</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01963.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Estimating Brownian motion dispersal rate, longevity and population density from spatially explicit mark–recapture data on tropical butterflies</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jarle Tufto</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Russell Lande</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thor-Harald Ringsby</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Steinar Engen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bernt-Erik Sæther</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas R. Walla</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Philip J. DeVries</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-09T12:29:48.359073-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01963.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01963.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01963.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> We develop a Bayesian method for analysing mark–recapture data in continuous habitat using a model in which individuals movement paths are Brownian motions, life spans are exponentially distributed and capture events occur at given instants in time if individuals are within a certain attractive distance of the traps.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> The joint posterior distribution of the dispersal rate, longevity, trap attraction distances and a number of latent variables representing the unobserved movement paths and time of death of all individuals is computed using Gibbs sampling.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> An estimate of absolute local population density is obtained simply by dividing the Poisson counts of individuals captured at given points in time by the estimated total attraction area of all traps. Our approach for estimating population density in continuous habitat avoids the need to define an arbitrary effective trapping area that characterized previous mark–recapture methods in continuous habitat.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We applied our method to estimate spatial demography parameters in nine species of neotropical butterflies. Path analysis of interspecific variation in demographic parameters and mean wing length revealed a simple network of strong causation. Larger wing length increases dispersal rate, which in turn increases trap attraction distance. However, higher dispersal rate also decreases longevity, thus explaining the surprising observation of a negative correlation between wing length and longevity.</p></div>]]></content:encoded><description>1. We develop a Bayesian method for analysing mark–recapture data in continuous habitat using a model in which individuals movement paths are Brownian motions, life spans are exponentially distributed and capture events occur at given instants in time if individuals are within a certain attractive distance of the traps.2. The joint posterior distribution of the dispersal rate, longevity, trap attraction distances and a number of latent variables representing the unobserved movement paths and time of death of all individuals is computed using Gibbs sampling.3. An estimate of absolute local population density is obtained simply by dividing the Poisson counts of individuals captured at given points in time by the estimated total attraction area of all traps. Our approach for estimating population density in continuous habitat avoids the need to define an arbitrary effective trapping area that characterized previous mark–recapture methods in continuous habitat.4. We applied our method to estimate spatial demography parameters in nine species of neotropical butterflies. Path analysis of interspecific variation in demographic parameters and mean wing length revealed a simple network of strong causation. Larger wing length increases dispersal rate, which in turn increases trap attraction distance. However, higher dispersal rate also decreases longevity, thus explaining the surprising observation of a negative correlation between wing length and longevity.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01960.x" xmlns="http://purl.org/rss/1.0/"><title>Topological plasticity increases robustness of mutualistic networks</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01960.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Topological plasticity increases robustness of mutualistic networks</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rodrigo Ramos-Jiliberto</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fernanda S. Valdovinos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pablo Moisset de Espanés</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">José D. Flores</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-07T14:24:46.609785-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01960.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01960.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01960.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Earlier studies used static models to evaluate the responses of mutualistic networks to external perturbations. Two classes of dynamics can be distinguished in ecological networks; population dynamics, represented mainly by changes in species abundances, and topological dynamics, represented by changes in the architecture of the web.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> In this study, we model the temporal evolution of three empirical plant–pollination networks incorporating both population and topological dynamics. We test the hypothesis that topological plasticity, realized through the ability of animals to rewire their connections after depletion of host abundances, enhances tolerance of mutualistic networks to species loss. We also compared the performance of various rewiring rules in affecting robustness.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> The results show that topological plasticity markedly increased the robustness of mutualistic networks. Our analyses also revealed that network robustness reached maximum levels when animals with less host plant availability were more likely to rewire. Also, preferential attachment to richer host plants, that is, to plants exhibiting higher abundance and few exploiters, enhances robustness more than other rewiring alternatives.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Our results highlight the potential role of topological plasticity in the robustness of mutualistic networks to species extinctions and suggest some plausible mechanisms by which the decisions of foragers may shape the collective dynamics of plant–pollinator systems.</p></div>]]></content:encoded><description>1. Earlier studies used static models to evaluate the responses of mutualistic networks to external perturbations. Two classes of dynamics can be distinguished in ecological networks; population dynamics, represented mainly by changes in species abundances, and topological dynamics, represented by changes in the architecture of the web.2. In this study, we model the temporal evolution of three empirical plant–pollination networks incorporating both population and topological dynamics. We test the hypothesis that topological plasticity, realized through the ability of animals to rewire their connections after depletion of host abundances, enhances tolerance of mutualistic networks to species loss. We also compared the performance of various rewiring rules in affecting robustness.3. The results show that topological plasticity markedly increased the robustness of mutualistic networks. Our analyses also revealed that network robustness reached maximum levels when animals with less host plant availability were more likely to rewire. Also, preferential attachment to richer host plants, that is, to plants exhibiting higher abundance and few exploiters, enhances robustness more than other rewiring alternatives.4. Our results highlight the potential role of topological plasticity in the robustness of mutualistic networks to species extinctions and suggest some plausible mechanisms by which the decisions of foragers may shape the collective dynamics of plant–pollinator systems.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01957.x" xmlns="http://purl.org/rss/1.0/"><title>Prey-race drives differentiation of biotypes in ant-eating spiders</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01957.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Prey-race drives differentiation of biotypes in ant-eating spiders</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">S. Pekár</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. Šmerda</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. Hrušková</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">O. Šedo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">C. Muster</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">P. Cardoso</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Z. Zdráhal</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">S. Korenko</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">P. Bureš</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">E. Líznarová</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">L. Sentenská</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-07T14:24:36.21832-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01957.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01957.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01957.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Disruptive natural selection resulting from specialization on different hosts is recognized as one of the most important driving forces in the diversification of herbivores and parasites. It has been proposed that a similar mechanism could apply to carnivorous predators too, although the evidence is still lacking.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Here, we show that the differentiation of biotypes of specialized ant-eating spiders of the genus <em>Zodarion</em> has probably been induced by prey-shifting. We focused on two forms of one species <em>Z. styliferum</em> from the Iberian Peninsula that presumably represent ecological races. We conducted geographic, ecological, venom-oriented, reproductive and genetic divergence analysis among multiple populations collected at a number of sites across Portugal and Madeira.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Geographic analysis revealed that the two forms occur in mosaic sympatry. Each form was found to associate in nature with a different ant species in a different habitat. Specifically, the <em>styliferum</em> form hunted predominantly <em>Messor</em> ants, and the <em>extraneum</em> form hunted mainly <em>Camponotus</em> ants. Laboratory experiments revealed that the two forms exhibit a significant preference for attacking focal ants, demonstrating higher paralysis efficiency, and also show different venom composition. Cross-mating of the two forms was significantly less likely than between pairs of the same form, suggesting moderate assortative mating. Phylogenetic analyses indicate low genetic differentiation of the two forms and parallel-repeated evolution of biotypes.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Adaptive prey-shifting correlated with habitat preference are at present the most valid explanations for biotype formation in <em>Zodarion</em>. The speciation of ant-eating <em>Zodarion</em> spiders thus appears to follow a scenario similar to that of host-shifting in parasites and herbivores.</p></div>]]></content:encoded><description>1. Disruptive natural selection resulting from specialization on different hosts is recognized as one of the most important driving forces in the diversification of herbivores and parasites. It has been proposed that a similar mechanism could apply to carnivorous predators too, although the evidence is still lacking.2. Here, we show that the differentiation of biotypes of specialized ant-eating spiders of the genus Zodarion has probably been induced by prey-shifting. We focused on two forms of one species Z. styliferum from the Iberian Peninsula that presumably represent ecological races. We conducted geographic, ecological, venom-oriented, reproductive and genetic divergence analysis among multiple populations collected at a number of sites across Portugal and Madeira.3. Geographic analysis revealed that the two forms occur in mosaic sympatry. Each form was found to associate in nature with a different ant species in a different habitat. Specifically, the styliferum form hunted predominantly Messor ants, and the extraneum form hunted mainly Camponotus ants. Laboratory experiments revealed that the two forms exhibit a significant preference for attacking focal ants, demonstrating higher paralysis efficiency, and also show different venom composition. Cross-mating of the two forms was significantly less likely than between pairs of the same form, suggesting moderate assortative mating. Phylogenetic analyses indicate low genetic differentiation of the two forms and parallel-repeated evolution of biotypes.4. Adaptive prey-shifting correlated with habitat preference are at present the most valid explanations for biotype formation in Zodarion. The speciation of ant-eating Zodarion spiders thus appears to follow a scenario similar to that of host-shifting in parasites and herbivores.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01961.x" xmlns="http://purl.org/rss/1.0/"><title>Spatial variation in egg size and egg number reflects trade-offs and bet-hedging in a freshwater fish</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01961.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Spatial variation in egg size and egg number reflects trade-offs and bet-hedging in a freshwater fish</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John R. Morrongiello</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nicholas R. Bond</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David A. Crook</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bob B. M. Wong</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-06T15:30:31.857982-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01961.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01961.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01961.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Maternal reproductive investment is thought to reflect a trade-off between offspring size and fecundity, and models generally predict that mothers inhabiting adverse environments will produce fewer, larger offspring. More recently, the importance of environmental unpredictability in influencing maternal investment has been considered, with some models predicting that mothers should adopt a diversified bet-hedging strategy whilst others a conservative bet-hedging strategy.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We explore spatial egg size and fecundity patterns in the freshwater fish southern pygmy perch (<em>Nannoperca australis</em>) that inhabits a diversity of streams along gradients of environmental quality, variability and predictability.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Contrary to some predictions, <em>N. australis</em> populations inhabiting increasingly harsh streams produced more numerous and smaller eggs. Furthermore, within-female egg size variability increased as environments became more unpredictable.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We argue that in harsh environments or those prone to physical disturbance, sources of mortality are size independent with offspring size having only a minor influence on offspring fitness. Instead, maternal fitness is maximized by producing many small eggs, increasing the likelihood that some offspring will disperse to permanent water. We also provide empirical support for diversified bet-hedging as an adaptive strategy when future environmental quality is uncertain and suggest egg size may be a more appropriate fitness measure in stable environments characterized by size-dependent fitness. These results <b>l</b>ikely reflect spatial patterns of adaptive plasticity and bet-hedging in response to both predictable and unpredictable environmental variance and highlight the importance of considering both trait averages and variance.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Reproductive life-history traits can vary predictably along environmental gradients. Human activity, such as the hydrological modification of natural flow regimes, alters the form and magnitude of these gradients, and this can have both ecological and evolutionary implications for biota adapted to now non-existent natural environmental heterogeneity.</p></div>]]></content:encoded><description>1. Maternal reproductive investment is thought to reflect a trade-off between offspring size and fecundity, and models generally predict that mothers inhabiting adverse environments will produce fewer, larger offspring. More recently, the importance of environmental unpredictability in influencing maternal investment has been considered, with some models predicting that mothers should adopt a diversified bet-hedging strategy whilst others a conservative bet-hedging strategy.2. We explore spatial egg size and fecundity patterns in the freshwater fish southern pygmy perch (Nannoperca australis) that inhabits a diversity of streams along gradients of environmental quality, variability and predictability.3. Contrary to some predictions, N. australis populations inhabiting increasingly harsh streams produced more numerous and smaller eggs. Furthermore, within-female egg size variability increased as environments became more unpredictable.4. We argue that in harsh environments or those prone to physical disturbance, sources of mortality are size independent with offspring size having only a minor influence on offspring fitness. Instead, maternal fitness is maximized by producing many small eggs, increasing the likelihood that some offspring will disperse to permanent water. We also provide empirical support for diversified bet-hedging as an adaptive strategy when future environmental quality is uncertain and suggest egg size may be a more appropriate fitness measure in stable environments characterized by size-dependent fitness. These results likely reflect spatial patterns of adaptive plasticity and bet-hedging in response to both predictable and unpredictable environmental variance and highlight the importance of considering both trait averages and variance.5. Reproductive life-history traits can vary predictably along environmental gradients. Human activity, such as the hydrological modification of natural flow regimes, alters the form and magnitude of these gradients, and this can have both ecological and evolutionary implications for biota adapted to now non-existent natural environmental heterogeneity.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01959.x" xmlns="http://purl.org/rss/1.0/"><title>Social environment affects juvenile dispersal in great tits (Parus major)</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01959.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Social environment affects juvenile dispersal in great tits (Parus major)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marion Nicolaus</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stephanie P. M. Michler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kirsten M. Jalvingh</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Richard Ubels</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marco van der Velde</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jan Komdeur</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christiaan Both</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joost M. Tinbergen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-06T15:26:52.790502-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01959.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01959.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01959.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Habitat selection can affect individual fitness, and therefore, individuals are expected to assess habitat quality of potential breeding sites before settlement.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We investigated the role of social environment on juvenile dispersal behaviour in the great tit (<em>Parus major</em>). Two main contradictory hypotheses can be formulated regarding social effects on juvenile dispersal as follows: (i) High fledgling density and sex ratio may enhance the intensity of local (kin) competition and, therefore, reduce individual survival chance, enhance emigration and reduce settlement (‘repulsion’ hypothesis) (ii) Alternatively, high fledgling density and sex ratio may signal high-quality habitat or lead to aggregation and thus increase individual survival chance, reduce emigration and enhance settlement (‘attraction’ hypothesis).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> To disentangle positive from negative effects of high density and male-biased sex ratio on dispersal, we manipulated the social composition of the fledgling population in 12 semi-isolated nest-box areas (plots) via a change of fledgling density (low/high) as well as fledgling sex ratio (female-biased/balanced/male-biased) across 3 years. We then tested whether experimental variation in male and female fledgling densities affected variation in local survival, emigration and settlement of juveniles, and whether social effects on survival and dispersal support the ‘repulsion’ or ‘attraction’ hypothesis.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We found no experimental effects on local survival and emigration probabilities. However, consistent with the ‘attraction’ hypothesis, settlement was significantly and positively affected by local experimental sex ratio in each of the study years: both male and female juveniles avoided female-biased plots and settled more in plots that were balanced and male-biased the previous year.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our study provides unprecedented experimental evidence that local sex ratio plays a causal role in habitat selection. We suggest that settlers avoid female-biased plots because a high proportion of females may reflect the absence or the low quality of local resources in the habitat. Alternatively, male territory acquisition may be facilitated by a high local density of ‘candidate’ males, and therefore, juveniles were less successful in settling in female-biased plots.</p></div>]]></content:encoded><description>1. Habitat selection can affect individual fitness, and therefore, individuals are expected to assess habitat quality of potential breeding sites before settlement.2. We investigated the role of social environment on juvenile dispersal behaviour in the great tit (Parus major). Two main contradictory hypotheses can be formulated regarding social effects on juvenile dispersal as follows: (i) High fledgling density and sex ratio may enhance the intensity of local (kin) competition and, therefore, reduce individual survival chance, enhance emigration and reduce settlement (‘repulsion’ hypothesis) (ii) Alternatively, high fledgling density and sex ratio may signal high-quality habitat or lead to aggregation and thus increase individual survival chance, reduce emigration and enhance settlement (‘attraction’ hypothesis).3. To disentangle positive from negative effects of high density and male-biased sex ratio on dispersal, we manipulated the social composition of the fledgling population in 12 semi-isolated nest-box areas (plots) via a change of fledgling density (low/high) as well as fledgling sex ratio (female-biased/balanced/male-biased) across 3 years. We then tested whether experimental variation in male and female fledgling densities affected variation in local survival, emigration and settlement of juveniles, and whether social effects on survival and dispersal support the ‘repulsion’ or ‘attraction’ hypothesis.4. We found no experimental effects on local survival and emigration probabilities. However, consistent with the ‘attraction’ hypothesis, settlement was significantly and positively affected by local experimental sex ratio in each of the study years: both male and female juveniles avoided female-biased plots and settled more in plots that were balanced and male-biased the previous year.5. Our study provides unprecedented experimental evidence that local sex ratio plays a causal role in habitat selection. We suggest that settlers avoid female-biased plots because a high proportion of females may reflect the absence or the low quality of local resources in the habitat. Alternatively, male territory acquisition may be facilitated by a high local density of ‘candidate’ males, and therefore, juveniles were less successful in settling in female-biased plots.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01953.x" xmlns="http://purl.org/rss/1.0/"><title>Trade-offs between offspring fitness and future reproduction of adult female black brent</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01953.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Trade-offs between offspring fitness and future reproduction of adult female black brent</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christopher A. Nicolai</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">James S. Sedinger</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-03T13:34:26.826499-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01953.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01953.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01953.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Successful reproduction requires numerous decisions, and some of which may require trade-offs between current and future reproduction. We studied effects of choice of foraging patches on gosling growth and future breeding by mothers in black brent (<em>Branta bernicla nigricans</em>) geese.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Specific foraging areas consistently produced high-quality goslings over 21 years. We found a consistent ranking of gosling mass, corrected for age, across brood rearing areas (BRAs) and years [Akaike model weights, Σ<em>w</em><sub><em>i</em></sub><em> </em>= 1·00 for models including additive effects of BRA and year]. Growth of goslings largely determines their future fitness, so areas where goslings grew most rapidly also produced goslings with the highest mean fitness.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We used a multistate robust design capture–mark–recapture approach to estimate the probability of transitioning from a breeding state to a non-breeding (unobservable) state as a function of quality of BRA.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> In the best supported model, transition from a breeding state to a non-breeding state was positively related to gosling growth rates across BRAs. Thus, future reproduction was lower for females using BRAs that produced higher-quality goslings. Our results are consistent with trade-offs by individual brent between fitness of their current offspring and their own reproductive value.</p></div>]]></content:encoded><description>1. Successful reproduction requires numerous decisions, and some of which may require trade-offs between current and future reproduction. We studied effects of choice of foraging patches on gosling growth and future breeding by mothers in black brent (Branta bernicla nigricans) geese.2. Specific foraging areas consistently produced high-quality goslings over 21 years. We found a consistent ranking of gosling mass, corrected for age, across brood rearing areas (BRAs) and years [Akaike model weights, Σwi = 1·00 for models including additive effects of BRA and year]. Growth of goslings largely determines their future fitness, so areas where goslings grew most rapidly also produced goslings with the highest mean fitness.3. We used a multistate robust design capture–mark–recapture approach to estimate the probability of transitioning from a breeding state to a non-breeding (unobservable) state as a function of quality of BRA.4. In the best supported model, transition from a breeding state to a non-breeding state was positively related to gosling growth rates across BRAs. Thus, future reproduction was lower for females using BRAs that produced higher-quality goslings. Our results are consistent with trade-offs by individual brent between fitness of their current offspring and their own reproductive value.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01952.x" xmlns="http://purl.org/rss/1.0/"><title>Are there trade-offs between pre- and post-fledging survival in black brent geese?</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01952.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Are there trade-offs between pre- and post-fledging survival in black brent geese?</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christopher A. Nicolai</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">James S. Sedinger</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-03T13:34:16.330417-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01952.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01952.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01952.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> The growth period is an important determinant of fitness later in life through its effects on first-year survival and future reproduction. Choices by adult females about where to rear their offspring strongly affect growth rates and offspring fitness in geese.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Individual female black brent (<em>Branta bernicla nigricans</em>) tend to raise their broods in the same areas each year, and these areas are consistently ranked with respect to growth rates of goslings. Therefore, some females consistently rear their broods on areas resulting in lower post-fledging fitness.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We explore the potential that growth rates of offspring (and associated fitness consequences) are traded off against other vital rates influencing fitness of either adult females or goslings. Growth of goslings primarily influences fitness after fledging, so one hypothesis is that survival before fledging, which is influenced by predation, is traded off against growth rates and post-fledging survival.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We estimated pre-fledging and post-fledging survival for goslings reared on areas used by broods from the Tutakoke River black brent colony. We examined recaptures, recoveries by hunters and resightings of brent marked as goslings with webtags and standard leg rings. These data were analyzed using capture–mark–recapture models in program <span class="smallCaps">mark</span> to derive separate estimates of pre- and post-fledging survival for 18 cohorts (1987–2004) of black brent goslings across seven brood rearing areas (BRAs).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Estimates of pre-fledging survival probability varied from 0·00 ± 0·00 (mean ± 95% confidence interval) to 0·92 ± 0·1; and estimates of post-fledging survival probability varied from 0·00 ± 0·00 to 1·00 ± 0·08. Substantial variation existed both among BRAs and years but post-fledging survival declined substantially during the study.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Pre- and post-fledging survival were positively correlated, exhibiting a quadratic relationship (ß<sub>post-fledging survival</sub> = 1·00 (±0·47)<em>x</em>−0·83 (±0·480)<em>x</em><sup>2</sup>, where <em>x</em> = pre-fledging survival). Therefore, we did not find a trade-off between pre- and post-fledging survival in black brent goslings across BRAs, suggesting that factors other than foraging conditions and predation on goslings must influence selection of BRAs.</p></div>]]></content:encoded><description>1. The growth period is an important determinant of fitness later in life through its effects on first-year survival and future reproduction. Choices by adult females about where to rear their offspring strongly affect growth rates and offspring fitness in geese.2. Individual female black brent (Branta bernicla nigricans) tend to raise their broods in the same areas each year, and these areas are consistently ranked with respect to growth rates of goslings. Therefore, some females consistently rear their broods on areas resulting in lower post-fledging fitness.3. We explore the potential that growth rates of offspring (and associated fitness consequences) are traded off against other vital rates influencing fitness of either adult females or goslings. Growth of goslings primarily influences fitness after fledging, so one hypothesis is that survival before fledging, which is influenced by predation, is traded off against growth rates and post-fledging survival.4. We estimated pre-fledging and post-fledging survival for goslings reared on areas used by broods from the Tutakoke River black brent colony. We examined recaptures, recoveries by hunters and resightings of brent marked as goslings with webtags and standard leg rings. These data were analyzed using capture–mark–recapture models in program mark to derive separate estimates of pre- and post-fledging survival for 18 cohorts (1987–2004) of black brent goslings across seven brood rearing areas (BRAs).5. Estimates of pre-fledging survival probability varied from 0·00 ± 0·00 (mean ± 95% confidence interval) to 0·92 ± 0·1; and estimates of post-fledging survival probability varied from 0·00 ± 0·00 to 1·00 ± 0·08. Substantial variation existed both among BRAs and years but post-fledging survival declined substantially during the study.6. Pre- and post-fledging survival were positively correlated, exhibiting a quadratic relationship (ßpost-fledging survival = 1·00 (±0·47)x−0·83 (±0·480)x2, where x = pre-fledging survival). Therefore, we did not find a trade-off between pre- and post-fledging survival in black brent goslings across BRAs, suggesting that factors other than foraging conditions and predation on goslings must influence selection of BRAs.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01950.x" xmlns="http://purl.org/rss/1.0/"><title>Seasonal cycles of species diversity and similarity in a tropical butterfly community</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01950.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Seasonal cycles of species diversity and similarity in a tropical butterfly community</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Vidar Grøtan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Russell Lande</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Steinar Engen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bernt-Erik Sæther</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Phil J. DeVries</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T15:25:25.957322-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01950.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01950.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01950.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Studies of seasonality in ecological diversity rarely extend over more than a few years, and few studies of seasonal diversity have explicitly investigated the influence of environmental factors on seasonal community composition, especially in tropical communities.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Our 10 years of monthly sampling in Amazonian Ecuador yielded 20 996 individuals of 137 fruit-feeding butterfly species. Seasonal cycles of rainfall drive annual cycles in species diversity and community similarity. Undetermined processes operating most strongly during the dry season maintain species diversity and high community similarity across years.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Seasonal cycles in community diversity and similarity are superimposed on a gradual decline in similarity between community samples on a decadal time-scale because of long-term changes in species abundances.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Monitoring and analysis of changes in community composition over a range of time-scales can be used to refine models of community dynamics by incorporating environmental factors necessary to predict the ecological impact of future climate change.</p></div>]]></content:encoded><description>1. Studies of seasonality in ecological diversity rarely extend over more than a few years, and few studies of seasonal diversity have explicitly investigated the influence of environmental factors on seasonal community composition, especially in tropical communities.2. Our 10 years of monthly sampling in Amazonian Ecuador yielded 20 996 individuals of 137 fruit-feeding butterfly species. Seasonal cycles of rainfall drive annual cycles in species diversity and community similarity. Undetermined processes operating most strongly during the dry season maintain species diversity and high community similarity across years.3. Seasonal cycles in community diversity and similarity are superimposed on a gradual decline in similarity between community samples on a decadal time-scale because of long-term changes in species abundances.4. Monitoring and analysis of changes in community composition over a range of time-scales can be used to refine models of community dynamics by incorporating environmental factors necessary to predict the ecological impact of future climate change.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01954.x" xmlns="http://purl.org/rss/1.0/"><title>Imported fire ants near the edge of their range: disturbance and moisture determine prevalence and impact of an invasive social insect</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01954.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Imported fire ants near the edge of their range: disturbance and moisture determine prevalence and impact of an invasive social insect</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Edward G. LeBrun</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert M. Plowes</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lawrence E. Gilbert</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-31T12:03:43.734297-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01954.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01954.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01954.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Habitat disturbance and species invasions interact in natural systems, making it difficult to isolate the primary cause of ecosystem degradation. A general understanding requires case studies of how disturbance and invasion interact across a variety of ecosystem – invasive species combinations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Dramatic losses in ant diversity followed the invasion of central Texas by red imported fire ants (<em>Solenopsis invicta</em>). However, recent manipulative studies in Florida revealed no effect on ant diversity following the removal of <em>S. invicta</em> from a disturbed pasture habitat, but moderate loss of diversity associated with their introduction into undisturbed habitat and no invasion occurred without disturbance. Thus, the importance of <em>S. invicta</em> in driving diversity loss and its ability to invade undisturbed systems is unresolved.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We examine the distribution and abundance of a large monogyne <em>S. invicta</em> population and its association with the co-occurring ant assemblage at a site in south Texas close to the aridity tolerance limit of <em>S. invicta</em>.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We document that moisture modulates <em>S. invicta</em> densities. Further, soil disturbing habitat manipulations greatly increase <em>S. invicta</em> population densities. However, <em>S. invicta</em> penetrates all habitats regardless of soil disturbance history. In contrast, controlled burns depress <em>S. invicta</em> densities.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> In habitats where <em>S. invicta</em> is prevalent, it completely replaces native fire ants. However, <em>S. invicta</em> impacts native ants as a whole less strongly. Intriguingly, native ants responded distinctly to <em>S. invicta</em> in different environments. In wet, undisturbed environments, high <em>S. invicta</em> abundance disrupts the spatial structure of the ant assemblage by increasing clumping and is associated with reduced species density, while in dry-disturbed habitats, sites with high <em>S. invicta</em> abundance possess high numbers of native species. Analyses of co-occurrence indicate that reduced species density in wet-undisturbed sites arises from negative species interactions between native ants and <em>S. invicta</em>. However, these same data suggest that the high native species density of abundant <em>S. invicta</em> sites in dry-disturbed environments does not result from facilitation.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Monogyne <em>S. invicta</em> populations play different roles in different environments, driving ant diversity loss in some, but being largely symptomatic of habitat disturbance in others.</p></div>]]></content:encoded><description>1. Habitat disturbance and species invasions interact in natural systems, making it difficult to isolate the primary cause of ecosystem degradation. A general understanding requires case studies of how disturbance and invasion interact across a variety of ecosystem – invasive species combinations.2. Dramatic losses in ant diversity followed the invasion of central Texas by red imported fire ants (Solenopsis invicta). However, recent manipulative studies in Florida revealed no effect on ant diversity following the removal of S. invicta from a disturbed pasture habitat, but moderate loss of diversity associated with their introduction into undisturbed habitat and no invasion occurred without disturbance. Thus, the importance of S. invicta in driving diversity loss and its ability to invade undisturbed systems is unresolved.3. We examine the distribution and abundance of a large monogyne S. invicta population and its association with the co-occurring ant assemblage at a site in south Texas close to the aridity tolerance limit of S. invicta.4. We document that moisture modulates S. invicta densities. Further, soil disturbing habitat manipulations greatly increase S. invicta population densities. However, S. invicta penetrates all habitats regardless of soil disturbance history. In contrast, controlled burns depress S. invicta densities.5. In habitats where S. invicta is prevalent, it completely replaces native fire ants. However, S. invicta impacts native ants as a whole less strongly. Intriguingly, native ants responded distinctly to S. invicta in different environments. In wet, undisturbed environments, high S. invicta abundance disrupts the spatial structure of the ant assemblage by increasing clumping and is associated with reduced species density, while in dry-disturbed habitats, sites with high S. invicta abundance possess high numbers of native species. Analyses of co-occurrence indicate that reduced species density in wet-undisturbed sites arises from negative species interactions between native ants and S. invicta. However, these same data suggest that the high native species density of abundant S. invicta sites in dry-disturbed environments does not result from facilitation.6. Monogyne S. invicta populations play different roles in different environments, driving ant diversity loss in some, but being largely symptomatic of habitat disturbance in others.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01951.x" xmlns="http://purl.org/rss/1.0/"><title>Complexity of multitrophic interactions in a grassland ecosystem depends on plant species diversity</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01951.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Complexity of multitrophic interactions in a grassland ecosystem depends on plant species diversity</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael Rzanny</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Winfried Voigt</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-31T12:03:33.219989-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01951.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01951.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01951.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> We studied the theoretical prediction that a loss of plant species richness has a strong impact on community interactions among all trophic levels and tested whether decreased plant species diversity results in a less complex structure and reduced interactions in ecological networks.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Using plant species-specific biomass and arthropod abundance data from experimental grassland plots (Jena Experiment), we constructed multitrophic functional group interaction webs to compare communities based on 4 and 16 plant species. 427 insect and spider species were classified into 13 functional groups. These functional groups represent the nodes of ecological networks. Direct and indirect interactions among them were assessed using partial Mantel tests. Interaction web complexity was quantified using three measures of network structure: connectance, interaction diversity and interaction strength.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Compared with high plant diversity plots, interaction webs based on low plant diversity plots showed reduced complexity in terms of total connectance, interaction diversity and mean interaction strength. Plant diversity effects obviously cascade up the food web and modify interactions across all trophic levels. The strongest effects occurred in interactions between adjacent trophic levels (i.e. predominantly trophic interactions), while significant interactions among plant and carnivore functional groups, as well as horizontal interactions (i.e. interactions between functional groups of the same trophic level), showed rather inconsistent responses and were generally rarer.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Reduced interaction diversity has the potential to decrease and destabilize ecosystem processes. Therefore, we conclude that the loss of basal producer species leads to more simple structured, less and more loosely connected species assemblages, which in turn are very likely to decrease ecosystem functioning, community robustness and tolerance to disturbance. Our results suggest that the functioning of the entire ecological community is critically linked to the diversity of its component plants species.</p></div>]]></content:encoded><description>1. We studied the theoretical prediction that a loss of plant species richness has a strong impact on community interactions among all trophic levels and tested whether decreased plant species diversity results in a less complex structure and reduced interactions in ecological networks.2. Using plant species-specific biomass and arthropod abundance data from experimental grassland plots (Jena Experiment), we constructed multitrophic functional group interaction webs to compare communities based on 4 and 16 plant species. 427 insect and spider species were classified into 13 functional groups. These functional groups represent the nodes of ecological networks. Direct and indirect interactions among them were assessed using partial Mantel tests. Interaction web complexity was quantified using three measures of network structure: connectance, interaction diversity and interaction strength.3. Compared with high plant diversity plots, interaction webs based on low plant diversity plots showed reduced complexity in terms of total connectance, interaction diversity and mean interaction strength. Plant diversity effects obviously cascade up the food web and modify interactions across all trophic levels. The strongest effects occurred in interactions between adjacent trophic levels (i.e. predominantly trophic interactions), while significant interactions among plant and carnivore functional groups, as well as horizontal interactions (i.e. interactions between functional groups of the same trophic level), showed rather inconsistent responses and were generally rarer.4. Reduced interaction diversity has the potential to decrease and destabilize ecosystem processes. Therefore, we conclude that the loss of basal producer species leads to more simple structured, less and more loosely connected species assemblages, which in turn are very likely to decrease ecosystem functioning, community robustness and tolerance to disturbance. Our results suggest that the functioning of the entire ecological community is critically linked to the diversity of its component plants species.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01948.x" xmlns="http://purl.org/rss/1.0/"><title>Habitat use throughout migration: linking individual consistency, prior breeding success and future breeding potential</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01948.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Habitat use throughout migration: linking individual consistency, prior breeding success and future breeding potential</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bethany J. Hoye</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Steffen Hahn</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bart A. Nolet</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marcel Klaassen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-24T13:53:11.488295-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01948.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01948.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01948.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Habitat use can influence individual performance in a wide range of animals, either immediately or through carry-over effects in subsequent seasons. Given that many animal species also show consistent individual differences in reproductive success, it seems plausible that individuals may have consistent patterns of habitat use representing individual specializations, with concomitant fitness consequences.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Stable-carbon isotope ratios from a range of tissues were used to discern individual consistency in habitat use along a terrestrial–aquatic gradient in a long-distance migrant, the Bewick’s swan (<em>Cygnus columbianus bewickii</em>). These individual specialisations represented &lt;15% of the isotopic breadth of the population for the majority of individuals and were seen to persist throughout autumn migration and overwintering until aquatic habitats were no longer available.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Individual foraging specialisations were then used to demonstrate two consecutive carry-over effects associated with macroscale habitat segregation: consequences of breeding season processes for autumn habitat use; and consequences of autumn habitat use for future reproductive success. Adults that were successful breeders in the year of capture used terrestrial habitats significantly more than adults that were not successful, revealing a substantial cost of reproduction and extended parental care. Use of aquatic habitats during autumn was, however, associated with increased body condition prior to spring migration; and increased subsequent breeding success in adults that had been unsuccessful the year before. Yet adults that were successful breeders in the year of capture remained the most likely to be successful the following year, despite their use of terrestrial habitats.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Our results uniquely demonstrate not only individual foraging specializations throughout the migration period, but also that processes during breeding and autumn migration, mediated by individual consistency, may play a fundamental role in the population dynamics of long-distance migrants. These findings, therefore, highlight the importance of long-term consistency to our understanding of habitat function, interindividual differences in fitness, population dynamics and the evolution of migratory strategies.</p></div>]]></content:encoded><description>1. Habitat use can influence individual performance in a wide range of animals, either immediately or through carry-over effects in subsequent seasons. Given that many animal species also show consistent individual differences in reproductive success, it seems plausible that individuals may have consistent patterns of habitat use representing individual specializations, with concomitant fitness consequences.2. Stable-carbon isotope ratios from a range of tissues were used to discern individual consistency in habitat use along a terrestrial–aquatic gradient in a long-distance migrant, the Bewick’s swan (Cygnus columbianus bewickii). These individual specialisations represented &lt;15% of the isotopic breadth of the population for the majority of individuals and were seen to persist throughout autumn migration and overwintering until aquatic habitats were no longer available.3. Individual foraging specialisations were then used to demonstrate two consecutive carry-over effects associated with macroscale habitat segregation: consequences of breeding season processes for autumn habitat use; and consequences of autumn habitat use for future reproductive success. Adults that were successful breeders in the year of capture used terrestrial habitats significantly more than adults that were not successful, revealing a substantial cost of reproduction and extended parental care. Use of aquatic habitats during autumn was, however, associated with increased body condition prior to spring migration; and increased subsequent breeding success in adults that had been unsuccessful the year before. Yet adults that were successful breeders in the year of capture remained the most likely to be successful the following year, despite their use of terrestrial habitats.4. Our results uniquely demonstrate not only individual foraging specializations throughout the migration period, but also that processes during breeding and autumn migration, mediated by individual consistency, may play a fundamental role in the population dynamics of long-distance migrants. These findings, therefore, highlight the importance of long-term consistency to our understanding of habitat function, interindividual differences in fitness, population dynamics and the evolution of migratory strategies.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01947.x" xmlns="http://purl.org/rss/1.0/"><title>Response of butterflies to structural and resource boundaries</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01947.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Response of butterflies to structural and resource boundaries</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Cheryl B. Schultz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Aldina M. A. Franco</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Elizabeth E. Crone</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-24T13:48:43.768113-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01947.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01947.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01947.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Two aspects of landscape composition shape the behavioural response of animals to habitat heterogeneity: physical habitat structure and abundance of key resources. In general, within-habitat movement behaviour has been investigated in relation to resources, and preference at boundaries has been quantified in response to physical structure.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Habitat preference studies suggest that responses to resources vs. structure should differ, e.g. between male and female animals, and effects of responses to structure and resources may also interact. However, most studies of animal movement combine various aspects of behavioural responses to ‘habitat’, implicitly assuming that resources and structure are broadly equivalent.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We conducted a large-scale experiment of the movement of Fender’s blue (<em>Icaricia icarioides fenderi</em>), an endangered butterfly, to investigate butterfly response to physical structure of the landscape (prairie, open woods and dense woods) and to resources [presence or absence of Kincaid’s lupine, <em>Lupinus oreganus</em> (larval hostplant patches)]. The experiment included 606 butterfly flight paths across four habitat types and nine ecotones.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Responses to physical structure and resource patches were not congruent. Butterflies were attracted to resource patches within both prairies and open woods and moved more slowly when in resource patches. Butterflies tended to prefer prairie at prairie-forest edges but tended to move faster in prairies than in open woods. Physical structure and resources also interacted; butterflies did not respond to physical habitat structure when resource patches spanned prairie – open woods ecotones.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Even dense woods were not perfect barriers, in contrast to a large body of literature that assumes insects from open habitats will not enter dense forests.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Movement of both males and females responded to resources and structure. However, female butterflies had stronger responses to both resources and structure in most cases. Females had strongest response to resource (hostplant) patches at patch edges, whereas the strongest preference of males was to return to prairie from open forest.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> If other species behave like Fender’s blue, then combining different definitions of ‘habitat’ (physical structure vs. resources), different aspects of movement (edge preference vs. within-habitat movement) and/or males and females within species could all lead to misleading conclusions. Our results highlight the importance of investigating these responses, and our study provides a framework for separating them in other systems.</p></div>]]></content:encoded><description>1. Two aspects of landscape composition shape the behavioural response of animals to habitat heterogeneity: physical habitat structure and abundance of key resources. In general, within-habitat movement behaviour has been investigated in relation to resources, and preference at boundaries has been quantified in response to physical structure.2. Habitat preference studies suggest that responses to resources vs. structure should differ, e.g. between male and female animals, and effects of responses to structure and resources may also interact. However, most studies of animal movement combine various aspects of behavioural responses to ‘habitat’, implicitly assuming that resources and structure are broadly equivalent.3. We conducted a large-scale experiment of the movement of Fender’s blue (Icaricia icarioides fenderi), an endangered butterfly, to investigate butterfly response to physical structure of the landscape (prairie, open woods and dense woods) and to resources [presence or absence of Kincaid’s lupine, Lupinus oreganus (larval hostplant patches)]. The experiment included 606 butterfly flight paths across four habitat types and nine ecotones.4. Responses to physical structure and resource patches were not congruent. Butterflies were attracted to resource patches within both prairies and open woods and moved more slowly when in resource patches. Butterflies tended to prefer prairie at prairie-forest edges but tended to move faster in prairies than in open woods. Physical structure and resources also interacted; butterflies did not respond to physical habitat structure when resource patches spanned prairie – open woods ecotones.5. Even dense woods were not perfect barriers, in contrast to a large body of literature that assumes insects from open habitats will not enter dense forests.6. Movement of both males and females responded to resources and structure. However, female butterflies had stronger responses to both resources and structure in most cases. Females had strongest response to resource (hostplant) patches at patch edges, whereas the strongest preference of males was to return to prairie from open forest.7. If other species behave like Fender’s blue, then combining different definitions of ‘habitat’ (physical structure vs. resources), different aspects of movement (edge preference vs. within-habitat movement) and/or males and females within species could all lead to misleading conclusions. Our results highlight the importance of investigating these responses, and our study provides a framework for separating them in other systems.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01942.x" xmlns="http://purl.org/rss/1.0/"><title>Quantitative analysis of compensatory and catch-up growth in diverse taxa</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01942.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Quantitative analysis of compensatory and catch-up growth in diverse taxa</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Katie L. Hector</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Shinichi Nakagawa</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-23T08:23:58.773894-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01942.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01942.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01942.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> ‘Compensatory growth’ and ‘catch-up growth’ are often used interchangeably to describe the faster than optimal growth that occurs following a period of dietary restriction in the development of many animals. Concerns about the statistical analysis of these studies have drawn attention to the risk of false detection in reports of compensatory and catch-up growth.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> This study aims to quantify the degree to which these compensatory responses occur across the animal kingdom. In addition, this study distinguishes the two terms, ‘compensatory growth’ and ‘catch-up growth’, to clarify the fitness consequences of rapid growth. Compensatory growth refers to a faster than usual growth rate, while catch-up growth implies attainment of control size.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Eight meta-analyses and meta-regression analyses were conducted on data extracted from 88 papers, including 11 taxonomic classes. The results confirmed that both growth tactics (i.e. compensatory and catch-up growth) occur across a wide range of taxa and result in decreased direct fitness components.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Importantly, the meta-analytic methods used made it possible to identify the specific experimental techniques that most successfully promoted rapid growth after restriction and key differences in the responses of the four major groups (mammals, birds, fish and arthropods) to dietary restriction. Endotherms are more likely to show a compensatory growth response because of their determinate growth; in contrast, the indeterminate and saltatory growth tactics of fish and arthropods reduce the pressure to rapidly achieve a large size.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Among the first meta-analyses to be conducted in this field, this study provides valuable support for the premises of compensatory and catch-up growth and also discusses weaknesses in experimental design, and possible solutions, in compensatory growth research. For example, we recommend conducting the experiment within the most linear phase of an animal’s growth to avoid analytical complications arising from size-dependent growth, and our results indicate that dietary dilution more closely resembles quantitative restriction than clutch size and intermittent feeding restriction methods when normal quantitative restriction is not possible.</p></div>]]></content:encoded><description>1. ‘Compensatory growth’ and ‘catch-up growth’ are often used interchangeably to describe the faster than optimal growth that occurs following a period of dietary restriction in the development of many animals. Concerns about the statistical analysis of these studies have drawn attention to the risk of false detection in reports of compensatory and catch-up growth.2. This study aims to quantify the degree to which these compensatory responses occur across the animal kingdom. In addition, this study distinguishes the two terms, ‘compensatory growth’ and ‘catch-up growth’, to clarify the fitness consequences of rapid growth. Compensatory growth refers to a faster than usual growth rate, while catch-up growth implies attainment of control size.3. Eight meta-analyses and meta-regression analyses were conducted on data extracted from 88 papers, including 11 taxonomic classes. The results confirmed that both growth tactics (i.e. compensatory and catch-up growth) occur across a wide range of taxa and result in decreased direct fitness components.4. Importantly, the meta-analytic methods used made it possible to identify the specific experimental techniques that most successfully promoted rapid growth after restriction and key differences in the responses of the four major groups (mammals, birds, fish and arthropods) to dietary restriction. Endotherms are more likely to show a compensatory growth response because of their determinate growth; in contrast, the indeterminate and saltatory growth tactics of fish and arthropods reduce the pressure to rapidly achieve a large size.5. Among the first meta-analyses to be conducted in this field, this study provides valuable support for the premises of compensatory and catch-up growth and also discusses weaknesses in experimental design, and possible solutions, in compensatory growth research. For example, we recommend conducting the experiment within the most linear phase of an animal’s growth to avoid analytical complications arising from size-dependent growth, and our results indicate that dietary dilution more closely resembles quantitative restriction than clutch size and intermittent feeding restriction methods when normal quantitative restriction is not possible.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01944.x" xmlns="http://purl.org/rss/1.0/"><title>Benefiting from a migratory prey: spatio-temporal patterns in allochthonous subsidization of an arctic predator</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01944.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Benefiting from a migratory prey: spatio-temporal patterns in allochthonous subsidization of an arctic predator</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marie-Andrée Giroux</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dominique Berteaux</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nicolas Lecomte</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Gilles Gauthier</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Guillaume Szor</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joël Bêty</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-23T05:48:58.31548-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01944.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01944.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01944.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Flows of nutrients and energy across ecosystem boundaries have the potential to subsidize consumer populations and modify the dynamics of food webs, but how spatio-temporal variations in autochthonous and allochthonous resources affect consumers’ subsidization remains largely unexplored.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We studied spatio-temporal patterns in the allochthonous subsidization of a predator living in a relatively simple ecosystem. We worked on Bylot Island (Nunavut, Canada), where arctic foxes (<em>Vulpes lagopus</em> L.) feed preferentially on lemmings (<em>Lemmus trimucronatus</em> and <em>Dicrostonyx groenlandicus</em> Traill), and alternatively on colonial greater snow geese (<em>Anser caerulescens atlanticus</em> L.). Geese migrate annually from their wintering grounds (where they feed on farmlands and marshes) to the Canadian Arctic, thus generating a strong flow of nutrients and energy across ecosystem boundaries.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We examined the influence of spatial variations in availability of geese on the diet of fox cubs (2003–2005) and on fox reproductive output (1996–2005) during different phases of the lemming cycle.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Using stable isotope analysis and a simple statistical routine developed to analyse the outputs of a multisource mixing model (SIAR), we showed that the contribution of geese to the diet of arctic fox cubs decreased with distance from the goose colony.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> The probability that a den was used for reproduction by foxes decreased with distance from the subsidized goose colony and increased with lemming abundance. When lemmings were highly abundant, the effect of distance from the colony disappeared. The goose colony thus generated a spatial patterning of reproduction probability of foxes, while the lemming cycle generated a strong temporal variation of reproduction probability of foxes.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> This study shows how the input of energy owing to the large-scale migration of prey affects the functional and reproductive responses of an opportunistic consumer, and how this input is spatially and temporally modulated through the foraging behaviour of the consumer. Thus, perspectives of both landscape and foraging ecology are needed to fully resolve the effects of subsidies on animal demographic processes and population dynamics.</p></div>]]></content:encoded><description>1. Flows of nutrients and energy across ecosystem boundaries have the potential to subsidize consumer populations and modify the dynamics of food webs, but how spatio-temporal variations in autochthonous and allochthonous resources affect consumers’ subsidization remains largely unexplored.2. We studied spatio-temporal patterns in the allochthonous subsidization of a predator living in a relatively simple ecosystem. We worked on Bylot Island (Nunavut, Canada), where arctic foxes (Vulpes lagopus L.) feed preferentially on lemmings (Lemmus trimucronatus and Dicrostonyx groenlandicus Traill), and alternatively on colonial greater snow geese (Anser caerulescens atlanticus L.). Geese migrate annually from their wintering grounds (where they feed on farmlands and marshes) to the Canadian Arctic, thus generating a strong flow of nutrients and energy across ecosystem boundaries.3. We examined the influence of spatial variations in availability of geese on the diet of fox cubs (2003–2005) and on fox reproductive output (1996–2005) during different phases of the lemming cycle.4. Using stable isotope analysis and a simple statistical routine developed to analyse the outputs of a multisource mixing model (SIAR), we showed that the contribution of geese to the diet of arctic fox cubs decreased with distance from the goose colony.5. The probability that a den was used for reproduction by foxes decreased with distance from the subsidized goose colony and increased with lemming abundance. When lemmings were highly abundant, the effect of distance from the colony disappeared. The goose colony thus generated a spatial patterning of reproduction probability of foxes, while the lemming cycle generated a strong temporal variation of reproduction probability of foxes.6. This study shows how the input of energy owing to the large-scale migration of prey affects the functional and reproductive responses of an opportunistic consumer, and how this input is spatially and temporally modulated through the foraging behaviour of the consumer. Thus, perspectives of both landscape and foraging ecology are needed to fully resolve the effects of subsidies on animal demographic processes and population dynamics.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01946.x" xmlns="http://purl.org/rss/1.0/"><title>Interspecific interactions drive cultural co-evolution and acoustic convergence in syntopic species</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01946.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Interspecific interactions drive cultural co-evolution and acoustic convergence in syntopic species</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paola Laiolo</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-19T10:43:37.870577-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01946.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01946.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01946.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Antagonistic interactions have been favourite subjects of studies on species co-evolution, because coexistence among competing species often results in quantifiable character displacement. A common output for competitive interactions is trait divergence, although the opposite phenomenon, convergence, has been proposed to evolve in some instances, for example in the communication behaviour of species that maintain mutually exclusive territories.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> I use here experimental and observational evidence to study how species interactions drive heterospecific signal convergence and analyse how convergence feeds back to the interaction itself, in the form of aggressive behaviour. I recorded the learned territorial signals of two non-hybridizing larks, <em>Galerida cristata</em> and <em>G. theklae</em>, and used allopatric populations as controls for evaluating acoustic convergence in syntopy. Acoustic variation was analysed with respect to social conditions controlling for other potential agents of natural selection, habitat and climate.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Interspecific convergence of <em>Galerida</em> calls peaked in syntopy. Although call acoustic structure was affected by climate and habitat, it matched gradients of density and proximity to congeners even at small local scales. The process of cultural transmission, in which individuals may acquire components of behaviour by copying neighbours, enhances the correlation between call acoustics and the local social milieu.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Territories were defended against both species, but playback stimuli of convergent congener calls elicited a stronger aggressive reaction than congener calls from allopatric locations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> This study shows that learned behaviours may co-evolve as a consequence of antagonistic interactions, determining reciprocal cultural evolution or cultural co-evolution. As for (biological) co-evolution, the distribution of competing species influences whether a particular area becomes a syntopic environment in which convergence is occurring, or an allopatric environment lacking interactions and reciprocal change. Because of their plastic nature, cultural coadaptations may rapidly shift in response to fluctuating social selection, thus propelling dynamic interactions and fine adjustments to the local environment.</p></div>]]></content:encoded><description>1. Antagonistic interactions have been favourite subjects of studies on species co-evolution, because coexistence among competing species often results in quantifiable character displacement. A common output for competitive interactions is trait divergence, although the opposite phenomenon, convergence, has been proposed to evolve in some instances, for example in the communication behaviour of species that maintain mutually exclusive territories.2. I use here experimental and observational evidence to study how species interactions drive heterospecific signal convergence and analyse how convergence feeds back to the interaction itself, in the form of aggressive behaviour. I recorded the learned territorial signals of two non-hybridizing larks, Galerida cristata and G. theklae, and used allopatric populations as controls for evaluating acoustic convergence in syntopy. Acoustic variation was analysed with respect to social conditions controlling for other potential agents of natural selection, habitat and climate.3. Interspecific convergence of Galerida calls peaked in syntopy. Although call acoustic structure was affected by climate and habitat, it matched gradients of density and proximity to congeners even at small local scales. The process of cultural transmission, in which individuals may acquire components of behaviour by copying neighbours, enhances the correlation between call acoustics and the local social milieu.4. Territories were defended against both species, but playback stimuli of convergent congener calls elicited a stronger aggressive reaction than congener calls from allopatric locations.5. This study shows that learned behaviours may co-evolve as a consequence of antagonistic interactions, determining reciprocal cultural evolution or cultural co-evolution. As for (biological) co-evolution, the distribution of competing species influences whether a particular area becomes a syntopic environment in which convergence is occurring, or an allopatric environment lacking interactions and reciprocal change. Because of their plastic nature, cultural coadaptations may rapidly shift in response to fluctuating social selection, thus propelling dynamic interactions and fine adjustments to the local environment.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01945.x" xmlns="http://purl.org/rss/1.0/"><title>Seasonal patterns of predation for gray wolves in the multi-prey system of Yellowstone National Park</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01945.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Seasonal patterns of predation for gray wolves in the multi-prey system of Yellowstone National Park</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Matthew C. Metz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Douglas W. Smith</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John A. Vucetich</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Daniel R. Stahler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rolf O. Peterson</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-19T10:43:03.4907-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01945.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01945.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01945.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> For large predators living in seasonal environments, patterns of predation are likely to vary among seasons because of related changes in prey vulnerability. Variation in prey vulnerability underlies the influence of predators on prey populations and the response of predators to seasonal variation in rates of biomass acquisition. Despite its importance, seasonal variation in predation is poorly understood.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We assessed seasonal variation in prey composition and kill rate for wolves <em>Canis lupus</em> living on the Northern Range (NR) of Yellowstone National Park. Our assessment was based on data collected over 14 winters (1995–2009) and five spring–summers between 2004 and 2009.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> The species composition of wolf-killed prey and the age and sex composition of wolf-killed elk <em>Cervus elaphus</em> (the primary prey for NR wolves) varied among seasons.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> One’s understanding of predation depends critically on the metric used to quantify kill rate. For example, kill rate was greatest in summer when quantified as the number of ungulates acquired per wolf per day, and least during summer when kill rate was quantified as the biomass acquired per wolf per day. This finding contradicts previous research that suggests that rates of biomass acquisition for large terrestrial carnivores tend not to vary among seasons.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Kill rates were not well correlated among seasons. For example, knowing that early-winter kill rate is higher than average (compared with other early winters) provides little basis for anticipating whether kill rates a few months later during late winter will be higher or lower than average (compared with other late winters). This observation indicates how observing, for example, higher-than-average kill rates throughout any particular season is an unreliable basis for inferring that the year-round average kill rate would be higher than average.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Our work shows how a large carnivore living in a seasonal environment displays marked seasonal variation in predation because of changes in prey vulnerability. Patterns of wolf predation were influenced by the nutritional condition of adult elk and the availability of smaller prey (i.e. elk calves, deer). We discuss how these patterns affect our overall understanding of predator and prey population dynamics.</p></div>]]></content:encoded><description>1. For large predators living in seasonal environments, patterns of predation are likely to vary among seasons because of related changes in prey vulnerability. Variation in prey vulnerability underlies the influence of predators on prey populations and the response of predators to seasonal variation in rates of biomass acquisition. Despite its importance, seasonal variation in predation is poorly understood.2. We assessed seasonal variation in prey composition and kill rate for wolves Canis lupus living on the Northern Range (NR) of Yellowstone National Park. Our assessment was based on data collected over 14 winters (1995–2009) and five spring–summers between 2004 and 2009.3. The species composition of wolf-killed prey and the age and sex composition of wolf-killed elk Cervus elaphus (the primary prey for NR wolves) varied among seasons.4. One’s understanding of predation depends critically on the metric used to quantify kill rate. For example, kill rate was greatest in summer when quantified as the number of ungulates acquired per wolf per day, and least during summer when kill rate was quantified as the biomass acquired per wolf per day. This finding contradicts previous research that suggests that rates of biomass acquisition for large terrestrial carnivores tend not to vary among seasons.5. Kill rates were not well correlated among seasons. For example, knowing that early-winter kill rate is higher than average (compared with other early winters) provides little basis for anticipating whether kill rates a few months later during late winter will be higher or lower than average (compared with other late winters). This observation indicates how observing, for example, higher-than-average kill rates throughout any particular season is an unreliable basis for inferring that the year-round average kill rate would be higher than average.6. Our work shows how a large carnivore living in a seasonal environment displays marked seasonal variation in predation because of changes in prey vulnerability. Patterns of wolf predation were influenced by the nutritional condition of adult elk and the availability of smaller prey (i.e. elk calves, deer). We discuss how these patterns affect our overall understanding of predator and prey population dynamics.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01941.x" xmlns="http://purl.org/rss/1.0/"><title>Wet season range fidelity in a tropical migratory ungulate</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01941.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Wet season range fidelity in a tropical migratory ungulate</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas A. Morrison</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Douglas T. Bolger</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-18T19:01:56.644224-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01941.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01941.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01941.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> In migratory populations, the degree of fidelity and dispersal among seasonal ranges is an important population process with consequences for demography, management, sensitivity to habitat change and adaptation to local environmental conditions.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Characterizing patterns of range fidelity in ungulates, however, has remained challenging because of the difficulties of following large numbers of marked individuals across multiple migratory cycles and of identifying the appropriate scale of analysis.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We examined fidelity to wet season (i.e. breeding) ranges in a recently declining population of wildebeest <em>Connochaetes taurinus</em> Burchell in northern Tanzania across 3 years. We used computer-assisted photographic identification and capture–recapture to characterize return patterns to three wet season ranges that were ecologically discrete and topographically isolated from one another.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Among 2557 uniquely identified adult wildebeest, we observed 150 recaptures across consecutive wet seasons. Between the two migratory subpopulations, the probability of remaining faithful to wet season areas ranged between 0·82 and 1·00. Animals from a non-migratory segment of the population (near Lake Manyara National Park) were rarely observed in other wet season ranges, despite proximity to one of the migratory pathways.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> We found no effect of sex on an individuals’ probability of switching wet season ranges. However, the breeding status of females in year <em>i</em> had a strong influence on patterns of range selection in year <em>i </em>+<em> </em>1, with surviving breeders over three times as likely to switch ranges as non-breeders.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Social-group associations between pairs of recaptured animals were random with respect to an individual’s wet season range during the previous or forthcoming wet seasons, suggesting that an individual’s herd identity during the dry season does not predict wet season range selection.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> Examining fidelity and dispersal in terrestrial migrations improves our understanding of the constraints that migrants experience when they face rapid habitat changes or fluctuations in environmental conditions.</p></div>]]></content:encoded><description>1. In migratory populations, the degree of fidelity and dispersal among seasonal ranges is an important population process with consequences for demography, management, sensitivity to habitat change and adaptation to local environmental conditions.2. Characterizing patterns of range fidelity in ungulates, however, has remained challenging because of the difficulties of following large numbers of marked individuals across multiple migratory cycles and of identifying the appropriate scale of analysis.3. We examined fidelity to wet season (i.e. breeding) ranges in a recently declining population of wildebeest Connochaetes taurinus Burchell in northern Tanzania across 3 years. We used computer-assisted photographic identification and capture–recapture to characterize return patterns to three wet season ranges that were ecologically discrete and topographically isolated from one another.4. Among 2557 uniquely identified adult wildebeest, we observed 150 recaptures across consecutive wet seasons. Between the two migratory subpopulations, the probability of remaining faithful to wet season areas ranged between 0·82 and 1·00. Animals from a non-migratory segment of the population (near Lake Manyara National Park) were rarely observed in other wet season ranges, despite proximity to one of the migratory pathways.5. We found no effect of sex on an individuals’ probability of switching wet season ranges. However, the breeding status of females in year i had a strong influence on patterns of range selection in year i + 1, with surviving breeders over three times as likely to switch ranges as non-breeders.6. Social-group associations between pairs of recaptured animals were random with respect to an individual’s wet season range during the previous or forthcoming wet seasons, suggesting that an individual’s herd identity during the dry season does not predict wet season range selection.7. Examining fidelity and dispersal in terrestrial migrations improves our understanding of the constraints that migrants experience when they face rapid habitat changes or fluctuations in environmental conditions.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01943.x" xmlns="http://purl.org/rss/1.0/"><title>Mutualistic cleaner fish initiate trait-mediated indirect interactions by influencing the behaviour of coral predators</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01943.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Mutualistic cleaner fish initiate trait-mediated indirect interactions by influencing the behaviour of coral predators</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas C. Adam</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-18T19:00:51.957981-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01943.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01943.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01943.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Indirect interactions resulting from changes in organismal traits such as behaviour [i.e. trait-mediated indirect interactions (TMIIs)] are widespread in biological communities, yet few studies have explored the potential for mutualisms to initiate TMIIs.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> This study used a combination of behavioural observations and manipulative field experiments to investigate potential TMIIs resulting from a mutualism between specialized cleaner fish and the ‘clients’ that visit cleaners for the removal of ectoparasites.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Behavioural observations indicate that the bluestreak cleaner wrasse, <em>Labroides dimidiatus,</em> increases local predation pressure on corals at cleaner stations by attracting corallivorous butterflyfish to their territories.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Observations of the ornate butterflyfish, <em>Chaetodon ornatissimus</em>, suggest a trade-off between seeking cleaning and foraging; individuals decreased their foraging rate at cleaner stations and shifted their diet to include a greater proportion of less preferred prey items. Nonetheless, predation pressure on corals was higher at cleaner stations because the spatial response of butterflyfish to cleaners more than compensated for their lower foraging rates.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> The results of a field experiment suggest that the greater predation pressure observed at cleaner stations may be sufficient to reduce the growth rate of the unpreferred coral <em>Porites rus</em>.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Together, these results emphasize the need to consider mutualists as potential initiators of TMIIs and highlight the importance of integrating individual movement into conceptual analyses of TMIIs.</p></div>]]></content:encoded><description>1. Indirect interactions resulting from changes in organismal traits such as behaviour [i.e. trait-mediated indirect interactions (TMIIs)] are widespread in biological communities, yet few studies have explored the potential for mutualisms to initiate TMIIs.2. This study used a combination of behavioural observations and manipulative field experiments to investigate potential TMIIs resulting from a mutualism between specialized cleaner fish and the ‘clients’ that visit cleaners for the removal of ectoparasites.3. Behavioural observations indicate that the bluestreak cleaner wrasse, Labroides dimidiatus, increases local predation pressure on corals at cleaner stations by attracting corallivorous butterflyfish to their territories.4. Observations of the ornate butterflyfish, Chaetodon ornatissimus, suggest a trade-off between seeking cleaning and foraging; individuals decreased their foraging rate at cleaner stations and shifted their diet to include a greater proportion of less preferred prey items. Nonetheless, predation pressure on corals was higher at cleaner stations because the spatial response of butterflyfish to cleaners more than compensated for their lower foraging rates.5. The results of a field experiment suggest that the greater predation pressure observed at cleaner stations may be sufficient to reduce the growth rate of the unpreferred coral Porites rus.6. Together, these results emphasize the need to consider mutualists as potential initiators of TMIIs and highlight the importance of integrating individual movement into conceptual analyses of TMIIs.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01940.x" xmlns="http://purl.org/rss/1.0/"><title>Sex recognition by odour and variation in the uropygial gland secretion in starlings</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01940.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Sex recognition by odour and variation in the uropygial gland secretion in starlings</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luisa Amo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jesús M. Avilés</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Deseada Parejo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Aránzazu Peña</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Juan Rodríguez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Gustavo Tomás</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-05T11:37:50.794221-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01940.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01940.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01940.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Although a growing body of evidence supports that olfaction based on chemical compounds emitted by birds may play a role in individual recognition, the possible role of chemical cues in sexual selection of birds has been only preliminarily studied.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We investigated for the first time whether a passerine bird, the spotless starling <em>Sturnus unicolor</em>, was able to discriminate the sex of conspecifics by using olfactory cues and whether the size and secretion composition of the uropygial gland convey information on sex, age and reproductive status in this species.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We performed a blind choice experiment during mating, and we found that starlings were able to discriminate the sex of conspecifics by using chemical cues alone. Both male and female starlings preferred male scents. Furthermore, the analysis of the chemical composition of the uropygial gland secretion by using gas chromatography–mass spectrometry (GC–MS) revealed differences between sexes, ages and reproductive status.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> In conclusion, our study reveals for first time that a passerine species can discriminate the sex of conspecifics by relying on chemical cues and suggests that the uropygial gland secretion may potentially function as a chemical signal used in mate choice and/or intrasexual competition in this species.</p></div>]]></content:encoded><description>1. Although a growing body of evidence supports that olfaction based on chemical compounds emitted by birds may play a role in individual recognition, the possible role of chemical cues in sexual selection of birds has been only preliminarily studied.2. We investigated for the first time whether a passerine bird, the spotless starling Sturnus unicolor, was able to discriminate the sex of conspecifics by using olfactory cues and whether the size and secretion composition of the uropygial gland convey information on sex, age and reproductive status in this species.3. We performed a blind choice experiment during mating, and we found that starlings were able to discriminate the sex of conspecifics by using chemical cues alone. Both male and female starlings preferred male scents. Furthermore, the analysis of the chemical composition of the uropygial gland secretion by using gas chromatography–mass spectrometry (GC–MS) revealed differences between sexes, ages and reproductive status.4. In conclusion, our study reveals for first time that a passerine species can discriminate the sex of conspecifics by relying on chemical cues and suggests that the uropygial gland secretion may potentially function as a chemical signal used in mate choice and/or intrasexual competition in this species.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01939.x" xmlns="http://purl.org/rss/1.0/"><title>Better off alone! Reproductive competition and ecological constraints determine sociality in the African striped mouse (Rhabdomys pumilio)</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01939.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Better off alone! Reproductive competition and ecological constraints determine sociality in the African striped mouse (Rhabdomys pumilio)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ivana Schoepf</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carsten Schradin</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-04T14:25:54.134941-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01939.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01939.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01939.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> While the reasons for group-living have been studied for decades, little is known about why individuals become solitary.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Several previous experimental studies could demonstrate that group-living can arises as a consequence of ecological constraints.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> It has been argued that reproductive competition between group members leads to significant costs of group-living, being a main reason of solitary-living. However, so far, no studies tested experimentally whether reproductive competition can explain solitary-living.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Using a socially flexible species, the African striped mouse (<em>Rhabdomys pumilio</em>), we tested experimentally in the field whether dispersal and solitary-living are more likely to occur when reproductive competition is present.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> We investigated ecological constraints, here expressed as a function of population density, by removing groups of striped mice and creating vacant territories. To control for the effect of reproductive competition, which occurs only during the breeding season, we performed experiments during both the breeding and the non-breeding season. This is the first removal experiment performed in a species with communal breeding during the non-breeding season.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> During the breeding season, when population density was low, more striped mice from experimental groups moved into the vacant territories and became solitary than striped mice from control groups. This is in support of the ecological constraints hypothesis.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> During the non-breeding season, striped mice remained group-living despite the availability of free territories. Significantly, more striped mice became solitary-living during the breeding than during the non-breeding season. This is the first experimental support for the reproductive competition hypothesis explaining solitary-living.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>8.</b> Analysis of the sexual maturity of males showed that males which became solitary had a higher reproductive potential than males that remained group-living. Analysis of the body mass data of females showed that more solitary females reproduced than group-living females. These results indicate that by becoming solitary individuals of both sexes avoided costs of reproductive competition within groups.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>9.</b> Our study provides experimental evidence that reproductive competition within groups can lead to dispersal and solitary-living.</p></div>]]></content:encoded><description>1. While the reasons for group-living have been studied for decades, little is known about why individuals become solitary.2. Several previous experimental studies could demonstrate that group-living can arises as a consequence of ecological constraints.3. It has been argued that reproductive competition between group members leads to significant costs of group-living, being a main reason of solitary-living. However, so far, no studies tested experimentally whether reproductive competition can explain solitary-living.4. Using a socially flexible species, the African striped mouse (Rhabdomys pumilio), we tested experimentally in the field whether dispersal and solitary-living are more likely to occur when reproductive competition is present.5. We investigated ecological constraints, here expressed as a function of population density, by removing groups of striped mice and creating vacant territories. To control for the effect of reproductive competition, which occurs only during the breeding season, we performed experiments during both the breeding and the non-breeding season. This is the first removal experiment performed in a species with communal breeding during the non-breeding season.6. During the breeding season, when population density was low, more striped mice from experimental groups moved into the vacant territories and became solitary than striped mice from control groups. This is in support of the ecological constraints hypothesis.7. During the non-breeding season, striped mice remained group-living despite the availability of free territories. Significantly, more striped mice became solitary-living during the breeding than during the non-breeding season. This is the first experimental support for the reproductive competition hypothesis explaining solitary-living.8. Analysis of the sexual maturity of males showed that males which became solitary had a higher reproductive potential than males that remained group-living. Analysis of the body mass data of females showed that more solitary females reproduced than group-living females. These results indicate that by becoming solitary individuals of both sexes avoided costs of reproductive competition within groups.9. Our study provides experimental evidence that reproductive competition within groups can lead to dispersal and solitary-living.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01938.x" xmlns="http://purl.org/rss/1.0/"><title>Species richness at the guild level: effects of species pool and local environmental conditions on stream macroinvertebrate communities</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01938.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Species richness at the guild level: effects of species pool and local environmental conditions on stream macroinvertebrate communities</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mira Grönroos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jani Heino</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-04T14:25:46.20182-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01938.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01938.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01938.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> A fundamental question in ecology is which factors determine species richness. Here, we studied the relative importance of regional species pool and local environmental characteristics in determining local species richness (LSR). Typically, this question has been studied using whole communities or a certain taxonomic group, although including species with widely varying biological traits in the same analysis may hinder the detection of ecologically meaningful patterns.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We studied the question above for whole stream macroinvertebrate community and within functional feeding guilds. We defined the local scale as a riffle site and the regional scale (i.e. representing the regional species pool) as a stream. Such intermediate-sized regional scale is rarely studied in this context.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We sampled altogether 100 sites, ten riffles (local scale) in each of ten streams (regional scale). We used the local-regional richness regression plots to study the overall effect of regional species pool on LSR. Variation partitioning was used to determine the relative importance of regional species pool and local environmental conditions for species richness.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> The local-regional richness relationship was mainly linear, suggesting strong species pool effects. Only one guild showed some signs of curvilinearity. However, variation partitioning showed that local environmental characteristics accounted for a larger fraction of variance in LSR than regional species pool. Also, the relative importance of the fractions differed between the whole community and guilds, as well as among guilds.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> This study indicates that the importance of the local and regional processes may vary depending on feeding guild and trophic level. We conclude that both the size of the regional species pool and local habitat characteristics are important in determining LSR of stream macroinvertebrates. Our results are in agreement with recent large-scale studies conducted in highly different study systems and complement the previous findings by showing that the interplay of regional and local factors is also important at intermediate regional scales.</p></div>]]></content:encoded><description>1. A fundamental question in ecology is which factors determine species richness. Here, we studied the relative importance of regional species pool and local environmental characteristics in determining local species richness (LSR). Typically, this question has been studied using whole communities or a certain taxonomic group, although including species with widely varying biological traits in the same analysis may hinder the detection of ecologically meaningful patterns.2. We studied the question above for whole stream macroinvertebrate community and within functional feeding guilds. We defined the local scale as a riffle site and the regional scale (i.e. representing the regional species pool) as a stream. Such intermediate-sized regional scale is rarely studied in this context.3. We sampled altogether 100 sites, ten riffles (local scale) in each of ten streams (regional scale). We used the local-regional richness regression plots to study the overall effect of regional species pool on LSR. Variation partitioning was used to determine the relative importance of regional species pool and local environmental conditions for species richness.4. The local-regional richness relationship was mainly linear, suggesting strong species pool effects. Only one guild showed some signs of curvilinearity. However, variation partitioning showed that local environmental characteristics accounted for a larger fraction of variance in LSR than regional species pool. Also, the relative importance of the fractions differed between the whole community and guilds, as well as among guilds.5. This study indicates that the importance of the local and regional processes may vary depending on feeding guild and trophic level. We conclude that both the size of the regional species pool and local habitat characteristics are important in determining LSR of stream macroinvertebrates. Our results are in agreement with recent large-scale studies conducted in highly different study systems and complement the previous findings by showing that the interplay of regional and local factors is also important at intermediate regional scales.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01936.x" xmlns="http://purl.org/rss/1.0/"><title>Reproductive responses to spatial and temporal prey availability in a coastal Arctic fox population</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01936.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Reproductive responses to spatial and temporal prey availability in a coastal Arctic fox population</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nina E. Eide</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Audun Stien</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pål Prestrud</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nigel G. Yoccoz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eva Fuglei</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-23T10:32:29.988112-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01936.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01936.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01936.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Input of external subsidies in the Arctic may have substantial effects on predator populations that otherwise would have been limited by low local primary productivity.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We explore life-history traits, age-specific fecundity, litter sizes and survival, and the population dynamics of an Arctic fox (<em>Vulpes lagopus</em>) population to explore the influence of the spatial distribution and temporal availability of its main prey; including both resident and migrating (external) prey resources.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> This study reveals that highly predictable cross-boundary subsidies from the marine food web, acting through seasonal access to seabirds, sustain larger local Arctic fox populations. Arctic fox dens located close to the coast in Svalbard were found to have higher occupancy rates, as expected from both high availability and high temporal and spatial predictability of prey resources (temporally stable external subsidies). Whereas the occupancy rate of inland dens varied between years in relation to the abundance of reindeer carcasses (temporally varying resident prey).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> With regard to demography, juvenile Arctic foxes in Svalbard have lower survival rates and a high age of first reproduction compared with other populations. We suggest this may be caused by a lack of unoccupied dens and a saturated population.</p></div>]]></content:encoded><description>1. Input of external subsidies in the Arctic may have substantial effects on predator populations that otherwise would have been limited by low local primary productivity.2. We explore life-history traits, age-specific fecundity, litter sizes and survival, and the population dynamics of an Arctic fox (Vulpes lagopus) population to explore the influence of the spatial distribution and temporal availability of its main prey; including both resident and migrating (external) prey resources.3. This study reveals that highly predictable cross-boundary subsidies from the marine food web, acting through seasonal access to seabirds, sustain larger local Arctic fox populations. Arctic fox dens located close to the coast in Svalbard were found to have higher occupancy rates, as expected from both high availability and high temporal and spatial predictability of prey resources (temporally stable external subsidies). Whereas the occupancy rate of inland dens varied between years in relation to the abundance of reindeer carcasses (temporally varying resident prey).4. With regard to demography, juvenile Arctic foxes in Svalbard have lower survival rates and a high age of first reproduction compared with other populations. We suggest this may be caused by a lack of unoccupied dens and a saturated population.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01937.x" xmlns="http://purl.org/rss/1.0/"><title>Life in varying environments: experimental evidence for delayed effects of juvenile environment on adult life history</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01937.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Life in varying environments: experimental evidence for delayed effects of juvenile environment on adult life history</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Heikki Helle</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Esa Koskela</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tapio Mappes</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-22T10:03:23.247121-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01937.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01937.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01937.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> The effects of environment experienced during early development on phenotype as an adult has started to gain vast amounts of interest in various taxa. Some evidence on long-term effects of juvenile environment is available, but replicated experimental studies in wild animals are still lacking.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Here we report the first replicated experiment in wild mammals which examines the long-term effects of juvenile and adult environments on individual fitness (reproduction, survival and health). The early development of bank vole (<em>Myodes glareolus</em>) individuals took place in either food-supplemented or un-supplemented outdoor enclosures. After the summer, adult individuals were reciprocally changed to either a similar or opposite resource environment to overwinter.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Adult environment had an overriding effect on reproductive success of females so that females overwintering in food-supplemented enclosures had a higher probability of breeding and advanced the initiation of breeding. However, the characteristics of their litters were determined by juvenile environment: females initially grown in food-supplemented conditions subsequently produced larger litters with bigger pups and a male-biased sex ratio.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> In males, individuals growing in un-supplemented conditions had the highest survival irrespective of adult environment during winter, whereas in females, neither the juvenile nor adult environments affected their survival significantly. The physiological condition of voles in spring, as determined by haematological parameters, was also differentially affected by juvenile (plasma proteins and male testosterone) and adult (haematocrit) environments.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our results suggest that (i) life-history trajectories of voles are not strictly specialized to a certain environment and (ii) the plastic life-history responses to present conditions can actually be caused by delayed effects of the juvenile environment. More generally, the results are important for understanding the mechanisms of delayed life-history effects as well as recognizing their population dynamic consequences.</p></div>]]></content:encoded><description>1. The effects of environment experienced during early development on phenotype as an adult has started to gain vast amounts of interest in various taxa. Some evidence on long-term effects of juvenile environment is available, but replicated experimental studies in wild animals are still lacking.2. Here we report the first replicated experiment in wild mammals which examines the long-term effects of juvenile and adult environments on individual fitness (reproduction, survival and health). The early development of bank vole (Myodes glareolus) individuals took place in either food-supplemented or un-supplemented outdoor enclosures. After the summer, adult individuals were reciprocally changed to either a similar or opposite resource environment to overwinter.3. Adult environment had an overriding effect on reproductive success of females so that females overwintering in food-supplemented enclosures had a higher probability of breeding and advanced the initiation of breeding. However, the characteristics of their litters were determined by juvenile environment: females initially grown in food-supplemented conditions subsequently produced larger litters with bigger pups and a male-biased sex ratio.4. In males, individuals growing in un-supplemented conditions had the highest survival irrespective of adult environment during winter, whereas in females, neither the juvenile nor adult environments affected their survival significantly. The physiological condition of voles in spring, as determined by haematological parameters, was also differentially affected by juvenile (plasma proteins and male testosterone) and adult (haematocrit) environments.5. Our results suggest that (i) life-history trajectories of voles are not strictly specialized to a certain environment and (ii) the plastic life-history responses to present conditions can actually be caused by delayed effects of the juvenile environment. More generally, the results are important for understanding the mechanisms of delayed life-history effects as well as recognizing their population dynamic consequences.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01935.x" xmlns="http://purl.org/rss/1.0/"><title>Seasonal shifts in predator body size diversity and trophic interactions in size-structured predator–prey systems</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01935.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Seasonal shifts in predator body size diversity and trophic interactions in size-structured predator–prey systems</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Volker H. W. Rudolf</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-22T10:03:19.195177-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01935.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01935.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01935.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Theory suggests that the relationship between predator diversity and prey suppression should depend on variation in predator traits such as body size, which strongly influences the type and strength of species interactions. Prey species often face a range of different sized predators, and the composition of body sizes of predators can vary between communities and within communities across seasons.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Here, I test how variation in size structure of predator communities influences prey survival using seasonal changes in the size structure of a cannibalistic population as a model system. Laboratory and field experiments showed that although the per-capita consumption rates increased at higher predator–prey size ratios, mortality rates did not consistently increase with average size of cannibalistic predators. Instead, prey mortality peaked at the highest level of predator body size diversity.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Furthermore, observed prey mortality was significantly higher than predictions from the null model that assumed no indirect interactions between predator size classes, indicating that different sized predators were not substitutable but had more than additive effects. Higher predator body size diversity therefore increased prey mortality, despite the increased potential for behavioural interference and predation among predators demonstrated in additional laboratory experiments.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Thus, seasonal changes in the distribution of predator body sizes altered the strength of prey suppression not only through changes in mean predator size but also through changes in the size distribution of predators. In general, this indicates that variation (i.e. diversity) within a single trait, body size, can influence the strength of trophic interactions and emphasizes the importance of seasonal shifts in size structure of natural food webs for community dynamics.</p></div>]]></content:encoded><description>1. Theory suggests that the relationship between predator diversity and prey suppression should depend on variation in predator traits such as body size, which strongly influences the type and strength of species interactions. Prey species often face a range of different sized predators, and the composition of body sizes of predators can vary between communities and within communities across seasons.2. Here, I test how variation in size structure of predator communities influences prey survival using seasonal changes in the size structure of a cannibalistic population as a model system. Laboratory and field experiments showed that although the per-capita consumption rates increased at higher predator–prey size ratios, mortality rates did not consistently increase with average size of cannibalistic predators. Instead, prey mortality peaked at the highest level of predator body size diversity.3. Furthermore, observed prey mortality was significantly higher than predictions from the null model that assumed no indirect interactions between predator size classes, indicating that different sized predators were not substitutable but had more than additive effects. Higher predator body size diversity therefore increased prey mortality, despite the increased potential for behavioural interference and predation among predators demonstrated in additional laboratory experiments.4. Thus, seasonal changes in the distribution of predator body sizes altered the strength of prey suppression not only through changes in mean predator size but also through changes in the size distribution of predators. In general, this indicates that variation (i.e. diversity) within a single trait, body size, can influence the strength of trophic interactions and emphasizes the importance of seasonal shifts in size structure of natural food webs for community dynamics.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01934.x" xmlns="http://purl.org/rss/1.0/"><title>Density dependence in group dynamics of a highly social mongoose, Suricata suricatta</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01934.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Density dependence in group dynamics of a highly social mongoose, Suricata suricatta</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Andrew W. Bateman</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Arpat Ozgul</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tim Coulson</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tim H. Clutton-Brock</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-24T10:25:46.954413-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01934.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01934.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01934.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> For social species, the link between individual behaviour and population dynamics is mediated by group-level demography.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Populations of obligate cooperative breeders are structured into social groups, which may be subject to inverse density dependence (Allee effects) that result from a dependence on conspecific helpers, but evidence for population-wide Allee effects is rare.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We use field data from a long-term study of cooperative meerkats (<em>Suricata suricatta</em>; Schreber, 1776) – a species for which local Allee effects are not reflected in population-level dynamics – to empirically model interannual group dynamics.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Using phenomenological population models, modified to incorporate environmental conditions and potential Allee effects, we first investigate overall patterns of group dynamics and find support only for conventional density dependence that increases after years of low rainfall.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> To explain the observed patterns, we examine specific demographic rates and assess their contributions to overall group dynamics. Although per-capita meerkat mortality is subject to a component Allee effect, it contributes relatively little to observed variation in group dynamics, and other (conventionally density dependent) demographic rates – especially emigration – govern group dynamics.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Our findings highlight the need to consider demographic processes and density dependence in subpopulations before drawing conclusions about how behaviour affects population processes in socially complex systems.</p></div>]]></content:encoded><description>1. For social species, the link between individual behaviour and population dynamics is mediated by group-level demography.2. Populations of obligate cooperative breeders are structured into social groups, which may be subject to inverse density dependence (Allee effects) that result from a dependence on conspecific helpers, but evidence for population-wide Allee effects is rare.3. We use field data from a long-term study of cooperative meerkats (Suricata suricatta; Schreber, 1776) – a species for which local Allee effects are not reflected in population-level dynamics – to empirically model interannual group dynamics.4. Using phenomenological population models, modified to incorporate environmental conditions and potential Allee effects, we first investigate overall patterns of group dynamics and find support only for conventional density dependence that increases after years of low rainfall.5. To explain the observed patterns, we examine specific demographic rates and assess their contributions to overall group dynamics. Although per-capita meerkat mortality is subject to a component Allee effect, it contributes relatively little to observed variation in group dynamics, and other (conventionally density dependent) demographic rates – especially emigration – govern group dynamics.6. Our findings highlight the need to consider demographic processes and density dependence in subpopulations before drawing conclusions about how behaviour affects population processes in socially complex systems.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01933.x" xmlns="http://purl.org/rss/1.0/"><title>Local sex ratio affects the cost of reproduction</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01933.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Local sex ratio affects the cost of reproduction</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marion Nicolaus</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stephanie P. M. Michler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Richard Ubels</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marco van der Velde</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Karen M. Bouwman</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christiaan Both</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joost M. Tinbergen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-23T10:19:02.255094-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01933.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01933.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01933.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Costs and benefits of reproduction are central to life-history theory, and the outcome of reproductive trade-offs may depend greatly on the ecological conditions in which they are estimated. In this study, we propose that costs and benefits of reproduction are modulated by social effects, and consequently that selection on reproductive rates depends on the social environment.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We tested this hypothesis in a great tit <em>Parus major</em> population. Over 3 years, we altered parental reproductive effort via brood size manipulations (small, intermediate, large) and manipulated the local social environment via changes in the local fledgling density (decreased, increased) and the local sex ratio (female-biased, control, male-biased).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We found that male-biased treatment consistently increased the subsequent local breeding densities over the 3-year study period. We also found that parents rearing small broods in these male-biased plots had increased survival rates compared with the other experimental groups.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We conclude that reproductive costs are the product of an interaction between parental phenotypic quality after reproduction and the social environment: raising a small brood had long-lasting effects on some phenotypic traits of the parents and that this increased their survival chances in male-biased environment where habitat quality may have deteriorated (via increased disease/predation risk or intraspecific competition).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our results provide the first experimental evidence that local sex ratio can affect reproductive costs and thus optimal clutch size.</p></div>]]></content:encoded><description>1. Costs and benefits of reproduction are central to life-history theory, and the outcome of reproductive trade-offs may depend greatly on the ecological conditions in which they are estimated. In this study, we propose that costs and benefits of reproduction are modulated by social effects, and consequently that selection on reproductive rates depends on the social environment.2. We tested this hypothesis in a great tit Parus major population. Over 3 years, we altered parental reproductive effort via brood size manipulations (small, intermediate, large) and manipulated the local social environment via changes in the local fledgling density (decreased, increased) and the local sex ratio (female-biased, control, male-biased).3. We found that male-biased treatment consistently increased the subsequent local breeding densities over the 3-year study period. We also found that parents rearing small broods in these male-biased plots had increased survival rates compared with the other experimental groups.4. We conclude that reproductive costs are the product of an interaction between parental phenotypic quality after reproduction and the social environment: raising a small brood had long-lasting effects on some phenotypic traits of the parents and that this increased their survival chances in male-biased environment where habitat quality may have deteriorated (via increased disease/predation risk or intraspecific competition).5. Our results provide the first experimental evidence that local sex ratio can affect reproductive costs and thus optimal clutch size.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01931.x" xmlns="http://purl.org/rss/1.0/"><title>Warming effects on consumption and intraspecific interference competition depend on predator metabolism</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01931.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Warming effects on consumption and intraspecific interference competition depend on predator metabolism</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Birgit Lang</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Björn C. Rall</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ulrich Brose</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-23T10:18:27.703149-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01931.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01931.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01931.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Model analyses show that the stability of population dynamics and food web persistence increase with the strength of interference competition. Despite this critical importance for community stability, little is known about how external factors such as the environmental temperature affect intraspecific interference competition.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We aimed to fill this void by studying the functional responses of two ground beetle species of different body size, <em>Pterostichus melanarius</em> and <em>Poecilus versicolor</em>. These functional response experiments were replicated across four predator densities and two temperatures to address the impact of temperature on intraspecific interference competition.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We generally expected that warming should increase the speed of movement, encounter rates and in consequence interference among predator individuals. In our experiment, this expectation was supported by the results obtained for the larger predator, <em>P. melanarius</em>, whereas the opposite pattern characterized the interference behaviour of the smaller predator <em>P. versicolor.</em></p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> These results suggest potentially nontrivial implications for the effects of environmental temperature on intraspecific interference competition, for which we propose an explanation based on the different sensitivity to warming of metabolic rates of both species. As expected, increasing temperature led to stronger interference competition of the larger species, <em>P. melanarius</em>, which exhibited a weaker increase in metabolic rate with increasing temperature. The stronger increase in the metabolic rate of the smaller predator, <em>P. versicolor</em>, had to be compensated by increasing searching activity for prey, which did not leave time for increasing interference.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Together, these results suggest that any generalization how interference competition responds to warming should also take the species’ metabolic response to temperature increases into account.</p></div>]]></content:encoded><description>1. Model analyses show that the stability of population dynamics and food web persistence increase with the strength of interference competition. Despite this critical importance for community stability, little is known about how external factors such as the environmental temperature affect intraspecific interference competition.2. We aimed to fill this void by studying the functional responses of two ground beetle species of different body size, Pterostichus melanarius and Poecilus versicolor. These functional response experiments were replicated across four predator densities and two temperatures to address the impact of temperature on intraspecific interference competition.3. We generally expected that warming should increase the speed of movement, encounter rates and in consequence interference among predator individuals. In our experiment, this expectation was supported by the results obtained for the larger predator, P. melanarius, whereas the opposite pattern characterized the interference behaviour of the smaller predator P. versicolor.4. These results suggest potentially nontrivial implications for the effects of environmental temperature on intraspecific interference competition, for which we propose an explanation based on the different sensitivity to warming of metabolic rates of both species. As expected, increasing temperature led to stronger interference competition of the larger species, P. melanarius, which exhibited a weaker increase in metabolic rate with increasing temperature. The stronger increase in the metabolic rate of the smaller predator, P. versicolor, had to be compensated by increasing searching activity for prey, which did not leave time for increasing interference.5. Together, these results suggest that any generalization how interference competition responds to warming should also take the species’ metabolic response to temperature increases into account.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01930.x" xmlns="http://purl.org/rss/1.0/"><title>Partitioning the effects of an ecosystem engineer: kangaroo rats control community structure via multiple pathways</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01930.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Partitioning the effects of an ecosystem engineer: kangaroo rats control community structure via multiple pathways</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Laura R. Prugh</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Justin S. Brashares</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-18T12:47:34.395289-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01930.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01930.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01930.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">no</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Ecosystem engineers impact communities by altering habitat conditions, but they can also have strong effects through consumptive, competitive and other non-engineering pathways.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Engineering effects can lead to fundamentally different community dynamics than non-engineering effects, but the relative strengths of these interactions are seldom quantified.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We combined structural equation modelling and exclosure experiments to partition the effects of a keystone engineer, the giant kangaroo rat (<em>Dipodomys ingens</em>), on plants, invertebrates and vertebrates in a semi-arid California grassland.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We separated the effects of burrow creation from kangaroo rat density and found that kangaroo rats increased the diversity and abundance of other species via both engineering and non-engineering pathways.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Engineering was the primary factor structuring plant and small mammal communities, whereas non-engineering effects structured invertebrate communities and increased lizard abundance.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> These results highlight the importance of the non-engineering effects of ecosystem engineers and shed new light on the multiple pathways by which strong-interactors shape communities.</p></div>]]></content:encoded><description>1. Ecosystem engineers impact communities by altering habitat conditions, but they can also have strong effects through consumptive, competitive and other non-engineering pathways.2. Engineering effects can lead to fundamentally different community dynamics than non-engineering effects, but the relative strengths of these interactions are seldom quantified.3. We combined structural equation modelling and exclosure experiments to partition the effects of a keystone engineer, the giant kangaroo rat (Dipodomys ingens), on plants, invertebrates and vertebrates in a semi-arid California grassland.4. We separated the effects of burrow creation from kangaroo rat density and found that kangaroo rats increased the diversity and abundance of other species via both engineering and non-engineering pathways.5. Engineering was the primary factor structuring plant and small mammal communities, whereas non-engineering effects structured invertebrate communities and increased lizard abundance.6. These results highlight the importance of the non-engineering effects of ecosystem engineers and shed new light on the multiple pathways by which strong-interactors shape communities.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01962.x" xmlns="http://purl.org/rss/1.0/"><title>The role of phylogeny in desert rodent community assembly</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01962.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The role of phylogeny in desert rodent community assembly</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">James H. Brown</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2012.01962.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2012.01962.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2012.01962.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">IN FOCUS</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">307</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">309</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<div class="para" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib" xmlns="http://www.w3.org/1999/xhtml"><div class="displayedItemText" id="fu1"><ul><li><img alt="image" src="http://onlinelibrary.wiley.com/store/10.1111/j.1365-2656.2012.01962.x/asset/image_n/JANE_1962_fu1.jpg?v=1&amp;t=gymkwmog&amp;s=295087c585260fa59b5e7935347c685fb5c66d5c"/></li></ul></div><p> [ Many landscapes span communities of varying degrees of biological complexity. Across such a gradient, diversity begets diversity. Increased environmental heterogeneity in the Mojave Desert increases the diversity of rodent consumers, in particular by allowing species that are phylogenetically more similar to coexist in more species rich communities. ]</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Stevens, R.D., Gavilanez, M.M., Tello, J.S. &amp; Ray, D.A. (2012) Phylogenetic structure illuminates the mechanistic role of environmental heterogeneity in community organization. <em>Journal of Animal Ecology</em>, <b>81</b>, 455–462.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>Recent advances in molecular genetics and phylogenetic reconstruction have the potential to transform ecology by providing new insights into the historical evolution of ecological communities. This study by Stevens and collaborators complements decades of previous research on desert rodents, by combining data from a field study and a phylogenetic tree for Mojave Desert rodents to address patterns and processes of community assembly. The number of coexisting rodent species is positively correlated, and the average phylogenetic distance among these species is negatively correlated with perennial plant species richness. As rodent species diversity increases along a gradient of increasing environmental heterogeneity, communities are composed of increasingly related species: there is a consistent pattern of phylogenetic structure from over-dispersed through random to clumped. I discuss this pattern in the light of complementary results of previous studies. This paper is noteworthy for calling attention to still unanswered questions about how the historical events of speciation, colonization, extinction, and trait evolution and their relationship to past climates and vegetation have given rise to current patterns of community organization. </b></p></div>]]></content:encoded><description> [ Many landscapes span communities of varying degrees of biological complexity. Across such a gradient, diversity begets diversity. Increased environmental heterogeneity in the Mojave Desert increases the diversity of rodent consumers, in particular by allowing species that are phylogenetically more similar to coexist in more species rich communities. ]Stevens, R.D., Gavilanez, M.M., Tello, J.S. &amp; Ray, D.A. (2012) Phylogenetic structure illuminates the mechanistic role of environmental heterogeneity in community organization. Journal of Animal Ecology, 81, 455–462.Recent advances in molecular genetics and phylogenetic reconstruction have the potential to transform ecology by providing new insights into the historical evolution of ecological communities. This study by Stevens and collaborators complements decades of previous research on desert rodents, by combining data from a field study and a phylogenetic tree for Mojave Desert rodents to address patterns and processes of community assembly. The number of coexisting rodent species is positively correlated, and the average phylogenetic distance among these species is negatively correlated with perennial plant species richness. As rodent species diversity increases along a gradient of increasing environmental heterogeneity, communities are composed of increasingly related species: there is a consistent pattern of phylogenetic structure from over-dispersed through random to clumped. I discuss this pattern in the light of complementary results of previous studies. This paper is noteworthy for calling attention to still unanswered questions about how the historical events of speciation, colonization, extinction, and trait evolution and their relationship to past climates and vegetation have given rise to current patterns of community organization. </description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01925.x" xmlns="http://purl.org/rss/1.0/"><title>Consumer–resource coupling in wet–dry tropical rivers</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01925.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Consumer–resource coupling in wet–dry tropical rivers</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Timothy D. Jardine</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Neil E. Pettit</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Danielle M. Warfe</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bradley J. Pusey</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Doug P. Ward</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael M. Douglas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Peter M. Davies</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stuart E. Bunn</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01925.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01925.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01925.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">310</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">322</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Despite implications for top-down and bottom-up control and the stability of food webs, understanding the links between consumers and their diets remains difficult, particularly in remote tropical locations where food resources are usually abundant and variable and seasonal hydrology produces alternating patterns of connectivity and isolation.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We used a large scale survey of freshwater biota from 67 sites in three catchments (Daly River, Northern Territory; Fitzroy River, Western Australia; and the Mitchell River, Queensland) in Australia’s wet–dry tropics and analysed stable isotopes of carbon (δ<sup>13</sup>C) to search for broad patterns in resource use by consumers in conjunction with known and measured indices of connectivity, the duration of floodplain inundation, and dietary choices (i.e. stomach contents of fish).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Regression analysis of biofilm δ<sup>13</sup>C against consumer δ<sup>13</sup>C, as an indicator of reliance on local food sources (periphyton and detritus), varied depending on taxa and catchment.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> The carbon isotope ratios of benthic invertebrates were tightly coupled to those of biofilm in all three catchments, suggesting assimilation of local resources by these largely nonmobile taxa.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Stable C isotope ratios of fish, however, were less well-linked to those of biofilm and varied by catchment according to hydrological connectivity; the perennially flowing Daly River with a long duration of floodplain inundation showed the least degree of coupling, the seasonally flowing Fitzroy River with an extremely short flood period showed the strongest coupling, and the Mitchell River was intermediate in connectivity, flood duration and consumer–resource coupling.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> These findings highlight the high mobility of the fish community in these rivers, and how hydrological connectivity between habitats drives patterns of consumer–resource coupling.</p></div>]]></content:encoded><description>1. Despite implications for top-down and bottom-up control and the stability of food webs, understanding the links between consumers and their diets remains difficult, particularly in remote tropical locations where food resources are usually abundant and variable and seasonal hydrology produces alternating patterns of connectivity and isolation.2. We used a large scale survey of freshwater biota from 67 sites in three catchments (Daly River, Northern Territory; Fitzroy River, Western Australia; and the Mitchell River, Queensland) in Australia’s wet–dry tropics and analysed stable isotopes of carbon (δ13C) to search for broad patterns in resource use by consumers in conjunction with known and measured indices of connectivity, the duration of floodplain inundation, and dietary choices (i.e. stomach contents of fish).3. Regression analysis of biofilm δ13C against consumer δ13C, as an indicator of reliance on local food sources (periphyton and detritus), varied depending on taxa and catchment.4. The carbon isotope ratios of benthic invertebrates were tightly coupled to those of biofilm in all three catchments, suggesting assimilation of local resources by these largely nonmobile taxa.5. Stable C isotope ratios of fish, however, were less well-linked to those of biofilm and varied by catchment according to hydrological connectivity; the perennially flowing Daly River with a long duration of floodplain inundation showed the least degree of coupling, the seasonally flowing Fitzroy River with an extremely short flood period showed the strongest coupling, and the Mitchell River was intermediate in connectivity, flood duration and consumer–resource coupling.6. These findings highlight the high mobility of the fish community in these rivers, and how hydrological connectivity between habitats drives patterns of consumer–resource coupling.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01917.x" xmlns="http://purl.org/rss/1.0/"><title>Rotifer population spread in relation to food, density and predation risk in an experimental system</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01917.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Rotifer population spread in relation to food, density and predation risk in an experimental system</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Daniel Kuefler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tal Avgar</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John M. Fryxell</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01917.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01917.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01917.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">323</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">329</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Despite the popular use of diffusion models to predict the spatial spread of populations over time, we currently know little about how diffusion rates change with the state of the environment or the internal condition of individuals. To address this gap in our understanding, we measured rates of spread for many populations of the rotifer <em>Brachionus calyciflorus</em> in a suite of well-replicated experiments.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> In one set of experiments, we manipulated food availability and population density along a continuous range of densities. In a second set, we manipulated the internal state of entire populations via food deprivation and exposure to predator kairomones.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Across replicate populations, diffusion rates were positively correlated with conspecific density. Diffusion rates were negatively correlated with food availability, especially when conspecific density was high. Diffusion rates of food-deprived populations or those exposed to predation risk were lower than controls.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Our results provide direct experimental evidence that rates of population spread are conditional on population density, food availability, body condition and predation risk.</p></div>]]></content:encoded><description>1. Despite the popular use of diffusion models to predict the spatial spread of populations over time, we currently know little about how diffusion rates change with the state of the environment or the internal condition of individuals. To address this gap in our understanding, we measured rates of spread for many populations of the rotifer Brachionus calyciflorus in a suite of well-replicated experiments.2. In one set of experiments, we manipulated food availability and population density along a continuous range of densities. In a second set, we manipulated the internal state of entire populations via food deprivation and exposure to predator kairomones.3. Across replicate populations, diffusion rates were positively correlated with conspecific density. Diffusion rates were negatively correlated with food availability, especially when conspecific density was high. Diffusion rates of food-deprived populations or those exposed to predation risk were lower than controls.4. Our results provide direct experimental evidence that rates of population spread are conditional on population density, food availability, body condition and predation risk.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01904.x" xmlns="http://purl.org/rss/1.0/"><title>Population regulation by habitat heterogeneity or individual adjustment?</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01904.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Population regulation by habitat heterogeneity or individual adjustment?</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Oliver Krüger</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nayden Chakarov</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jan T. Nielsen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Volkher Looft</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas Grünkorn</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bernd Struwe-Juhl</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Anders P. Møller</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01904.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01904.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01904.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">330</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">340</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> The habitat heterogeneity (HHH) and individual adjustment (IAH) hypotheses are commonly proposed to explain a decrease in reproduction rate with increasing population density. Higher numbers of low-quality territories with low reproductive success as density increases lead to a decrease in reproduction under the HHH, while more competition at high density decreases reproduction across all territories under the IAH.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We analyse the influence of density and habitat heterogeneity on reproductive success in eight populations of long-lived territorial birds of prey belonging to four species. Sufficient reliability in distinguishing between population-wide, site-specific and individual quality effects on reproduction was granted through the minimal duration of 20 years of all data sets and the ability to control for individual quality in five of them.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Density increased in five populations but reproduction did not decrease in these. Territory occupancy as a surrogate of territory quality correlated positively with reproductive success but only significantly so in large data sets with more than 100 territories.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Reproductive success was always best explained by measures of territory quality in multivariate models. Direct or delayed (<em>t</em>−1) population density entered very few of the best models. Mixed models controlling for individual quality showed an increasing reproductive performance in older individuals and in those laying earlier, but measures of territory quality were also always retained in the best models.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> We find strong support for the habitat heterogeneity hypothesis but weak support for the individual adjustment hypothesis. Both individual and site characteristics are crucial for reproductive performance in long-lived birds. Proportional occupancy of territories enables recognition of high-quality territories as preferential conservation targets.</p></div>]]></content:encoded><description>1. The habitat heterogeneity (HHH) and individual adjustment (IAH) hypotheses are commonly proposed to explain a decrease in reproduction rate with increasing population density. Higher numbers of low-quality territories with low reproductive success as density increases lead to a decrease in reproduction under the HHH, while more competition at high density decreases reproduction across all territories under the IAH.2. We analyse the influence of density and habitat heterogeneity on reproductive success in eight populations of long-lived territorial birds of prey belonging to four species. Sufficient reliability in distinguishing between population-wide, site-specific and individual quality effects on reproduction was granted through the minimal duration of 20 years of all data sets and the ability to control for individual quality in five of them.3. Density increased in five populations but reproduction did not decrease in these. Territory occupancy as a surrogate of territory quality correlated positively with reproductive success but only significantly so in large data sets with more than 100 territories.4. Reproductive success was always best explained by measures of territory quality in multivariate models. Direct or delayed (t−1) population density entered very few of the best models. Mixed models controlling for individual quality showed an increasing reproductive performance in older individuals and in those laying earlier, but measures of territory quality were also always retained in the best models.5. We find strong support for the habitat heterogeneity hypothesis but weak support for the individual adjustment hypothesis. Both individual and site characteristics are crucial for reproductive performance in long-lived birds. Proportional occupancy of territories enables recognition of high-quality territories as preferential conservation targets.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01915.x" xmlns="http://purl.org/rss/1.0/"><title>Reproductive synchrony in a recovering bottlenecked sea turtle population</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01915.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Reproductive synchrony in a recovering bottlenecked sea turtle population</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Virginie Plot</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Benoît de Thoisy</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stéphane Blanc</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Laurent Kelle</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Anne Lavergne</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hélène Roger-Bérubet</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Yann Tremblay</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sabrina Fossette</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jean-Yves Georges</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01915.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01915.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01915.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">341</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">351</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> The assessment of species extinction risk has been well established for some time now. Assessing the potential for recovery in endangered species is however much more challenging, because complementary approaches are required to detect reliable signals of positive trends.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> This study combines genetics, demography and behavioural data at three different time-scales to assess historical and recent population changes and evidence of reproductive synchrony in a small population of olive ridley sea turtle <em>Lepidochelys olivacea</em>. <em>Lepidochelys</em> is considered as the most extraordinary example of reproductive synchrony in reptiles, yet to date, it has only been reported in large populations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Using Bayesian coalescent-based models on microsatellite nuclear DNA variability, we demonstrate that effective population size in olive ridleys nesting in French Guiana has dramatically declined by 99% over the last 20 centuries. This low current population size is further illustrated by the absence of genetic mitochondrial DNA diversity in the present nesting population. Yet, monitoring of nesting sites in French Guiana suggests a possible recovery of the population over the last decade.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Satellite telemetry shows that over the first 14 days of their 28-days inter-nesting interval, i.e. when eggs maturation is likely to occur, gravid females disperse over the continental shelf. They then gather together with a striking spatiotemporal consistency close to the nesting site, where they later emerge for their second nesting event.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our results therefore suggest that reproductive synchrony also occurs in small populations. Olive ridleys may ensure this synchrony by adjusting the duration of the second half of their inter-nesting interval prior to landing, possibly through social mediation.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Such reproductive synchrony may be related to the maintenance of some species-specific strategy despite former collapse and may contribute to the present population recovery. The gregarious behaviour of reproductive individuals close to shore where human-induced perturbations occur is however a cause for conservation concern for this still poorly known species.</p></div>]]></content:encoded><description>1. The assessment of species extinction risk has been well established for some time now. Assessing the potential for recovery in endangered species is however much more challenging, because complementary approaches are required to detect reliable signals of positive trends.2. This study combines genetics, demography and behavioural data at three different time-scales to assess historical and recent population changes and evidence of reproductive synchrony in a small population of olive ridley sea turtle Lepidochelys olivacea. Lepidochelys is considered as the most extraordinary example of reproductive synchrony in reptiles, yet to date, it has only been reported in large populations.3. Using Bayesian coalescent-based models on microsatellite nuclear DNA variability, we demonstrate that effective population size in olive ridleys nesting in French Guiana has dramatically declined by 99% over the last 20 centuries. This low current population size is further illustrated by the absence of genetic mitochondrial DNA diversity in the present nesting population. Yet, monitoring of nesting sites in French Guiana suggests a possible recovery of the population over the last decade.4. Satellite telemetry shows that over the first 14 days of their 28-days inter-nesting interval, i.e. when eggs maturation is likely to occur, gravid females disperse over the continental shelf. They then gather together with a striking spatiotemporal consistency close to the nesting site, where they later emerge for their second nesting event.5. Our results therefore suggest that reproductive synchrony also occurs in small populations. Olive ridleys may ensure this synchrony by adjusting the duration of the second half of their inter-nesting interval prior to landing, possibly through social mediation.6. Such reproductive synchrony may be related to the maintenance of some species-specific strategy despite former collapse and may contribute to the present population recovery. The gregarious behaviour of reproductive individuals close to shore where human-induced perturbations occur is however a cause for conservation concern for this still poorly known species.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01918.x" xmlns="http://purl.org/rss/1.0/"><title>Survival and population size of a resident bird species are declining as temperature increases</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01918.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Survival and population size of a resident bird species are declining as temperature increases</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Leonard Santisteban</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Craig W. Benkman</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Trevor Fetz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Julie W. Smith</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01918.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01918.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01918.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">352</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">363</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> A large number of migratory bird species appear to be declining as the result of climate change, but whether resident bird species have or will be adversely affected by climate change is less clear. We focus on the South Hills crossbill (<em>Loxia curvirostra</em> complex), which is endemic to about 70 km<sup>2</sup> of Rocky Mountain lodgepole pine (<em>Pinus contorta latifolia</em>) forest in southern Idaho, USA.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Our results indicate that the South Hills crossbill has declined by over 60% between 2003 and 2008, and that decreasing adult survival drives this population decline.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We evaluated the relative support for multiple hypotheses linking crossbill survival to climate, an ectoparasitic mite (scaly-leg mites <em>Knemidokoptes jamaicensis</em>), and the recent emergence of West Nile virus. Changes in adult apparent survival rate were closely associated with average spring and annual temperatures, and with high temperatures (≥32 °C) during summer, which have increased during the last decade. In contrast, there was little evidence that scaly-leg mites or West Nile virus contributed to recent declines in adult survival.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> The most probable mechanism causing the decline in adult survival and population size is a decrease in the availability of their primary food resource, seeds in serotinous pine cones. Cone production has declined with increasing annual temperatures, and these cones appear to be prematurely opening owing to increasingly hot summer conditions releasing their seeds and reducing the carrying capacity for crossbills later in the year.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> In light of regional climate change forecasts, which include an increase in both annual temperature and hot days (&gt;32 °C), and the likely disappearance of lodgepole pine from southern Idaho by the end of this century, additional research is needed to determine how to maintain lodgepole pine forests and their supply of seeds to conserve one of the few bird species endemic to the continental United States.</p></div>]]></content:encoded><description>1. A large number of migratory bird species appear to be declining as the result of climate change, but whether resident bird species have or will be adversely affected by climate change is less clear. We focus on the South Hills crossbill (Loxia curvirostra complex), which is endemic to about 70 km2 of Rocky Mountain lodgepole pine (Pinus contorta latifolia) forest in southern Idaho, USA.2. Our results indicate that the South Hills crossbill has declined by over 60% between 2003 and 2008, and that decreasing adult survival drives this population decline.3. We evaluated the relative support for multiple hypotheses linking crossbill survival to climate, an ectoparasitic mite (scaly-leg mites Knemidokoptes jamaicensis), and the recent emergence of West Nile virus. Changes in adult apparent survival rate were closely associated with average spring and annual temperatures, and with high temperatures (≥32 °C) during summer, which have increased during the last decade. In contrast, there was little evidence that scaly-leg mites or West Nile virus contributed to recent declines in adult survival.4. The most probable mechanism causing the decline in adult survival and population size is a decrease in the availability of their primary food resource, seeds in serotinous pine cones. Cone production has declined with increasing annual temperatures, and these cones appear to be prematurely opening owing to increasingly hot summer conditions releasing their seeds and reducing the carrying capacity for crossbills later in the year.5. In light of regional climate change forecasts, which include an increase in both annual temperature and hot days (&gt;32 °C), and the likely disappearance of lodgepole pine from southern Idaho by the end of this century, additional research is needed to determine how to maintain lodgepole pine forests and their supply of seeds to conserve one of the few bird species endemic to the continental United States.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01913.x" xmlns="http://purl.org/rss/1.0/"><title>Density-dependence vs. density-independence – linking reproductive allocation to population abundance and vegetation greenness</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01913.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Density-dependence vs. density-independence – linking reproductive allocation to population abundance and vegetation greenness</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bård-Jørgen Bårdsen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Torkild Tveraa</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01913.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01913.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01913.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">364</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">376</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Recent studies have shown that optimal reproductive allocation depends on both climatic conditions and population density. We tested this hypothesis using six years of demographic data from eight reindeer (<em>Rangifer tarandus</em>) populations coupled with data on population abundance and vegetation greenness [measured using the Enhanced Vegetation Index (EVI)].</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Female spring body mass positively affected summer body mass gain, and lactating females were unable to compensate for harsh winters as efficiently as barren ones. Female spring body mass was highly sensitive to changes in population abundance and vegetation greenness and less dependent on previous autumn body mass and reproductive status. Lactating females were larger than barren females in the spring. Moreover, female autumn body mass was positively related to female autumn body mass and reproductive success and was not very sensitive to changes in vegetation greenness and population abundance.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Offspring autumn body mass was positively related to both maternal spring and autumn body mass, and as predicted from theory, offspring were more sensitive to changes in vegetation greenness and population abundance than adult females. A lagged cost of reproduction was present as larger females who were barren, the previous year produced larger offspring than equally sized females that successfully reproduced the previous year.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Reproductive success was negatively related to female autumn body mass and positively related to female spring body mass. Moreover, females who successfully reproduced the previous year experienced the highest reproductive success. The fact that negative density-dependence was only present for females that had successfully reproduced the previous year further support the hypothesis that reproduction is costly.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> This study shows that female reindeer buffer their reproductive allocation according to expected winter conditions and that their buffering abilities were limited by population abundance and a lagged cost of reproduction and enhanced by vegetation greenness.</p></div>]]></content:encoded><description>1. Recent studies have shown that optimal reproductive allocation depends on both climatic conditions and population density. We tested this hypothesis using six years of demographic data from eight reindeer (Rangifer tarandus) populations coupled with data on population abundance and vegetation greenness [measured using the Enhanced Vegetation Index (EVI)].2. Female spring body mass positively affected summer body mass gain, and lactating females were unable to compensate for harsh winters as efficiently as barren ones. Female spring body mass was highly sensitive to changes in population abundance and vegetation greenness and less dependent on previous autumn body mass and reproductive status. Lactating females were larger than barren females in the spring. Moreover, female autumn body mass was positively related to female autumn body mass and reproductive success and was not very sensitive to changes in vegetation greenness and population abundance.3. Offspring autumn body mass was positively related to both maternal spring and autumn body mass, and as predicted from theory, offspring were more sensitive to changes in vegetation greenness and population abundance than adult females. A lagged cost of reproduction was present as larger females who were barren, the previous year produced larger offspring than equally sized females that successfully reproduced the previous year.4. Reproductive success was negatively related to female autumn body mass and positively related to female spring body mass. Moreover, females who successfully reproduced the previous year experienced the highest reproductive success. The fact that negative density-dependence was only present for females that had successfully reproduced the previous year further support the hypothesis that reproduction is costly.5. This study shows that female reindeer buffer their reproductive allocation according to expected winter conditions and that their buffering abilities were limited by population abundance and a lagged cost of reproduction and enhanced by vegetation greenness.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01912.x" xmlns="http://purl.org/rss/1.0/"><title>Migratory stopover in the long-distance migrant silver-haired bat, Lasionycteris noctivagans</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01912.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Migratory stopover in the long-distance migrant silver-haired bat, Lasionycteris noctivagans</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Liam P. McGuire</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christopher G. Guglielmo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stuart A. Mackenzie</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Philip D. Taylor</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01912.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01912.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01912.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">377</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">385</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Some bat species make long-distance latitudinal migrations between summer and winter grounds, but because of their elusive nature, few aspects of their biology are well understood. The need for migratory stopover sites to rest and refuel, such as used by birds, has been repeatedly suggested, but not previously tested empirically in bats.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We studied migrating silver-haired bats (<em>Lasionycteris noctivagans</em>) at Long Point, ON, Canada. We used digital radio-transmitters to track 30 bats using an array of five towers that effectively covered the entire region (<em>c.</em> 20 × 40 km). We measured stopover duration and departure direction, and documented movement patterns, foraging activity and roost sites. We measured body composition on arrival using quantitative magnetic resonance and simulated long-distance migration using observed body composition to predict migration range and rate.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Migration occurred in two waves (late August and mid-September). Most bats stayed 1–2 days, although two remained &gt;2 weeks. One third of the bats foraged while at the site, many foraging opportunistically on nights when rain precluded continued migration. Bats roosted in a variety of tree species and manmade structures in natural and developed areas. Half of the bats departed across Lake Erie (minimum crossing distance <em>c.</em> 38 km) while half departed along the shoreline.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Simulations predicted a migration rate of <em>c.</em> 250–275 km per day and suggest that all but one of the bats in our study carried sufficient fuel stores to reach the putative wintering area (estimated distance 1500 km) without further refuelling.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our results suggest that migrating bats stopover for sanctuary or short-term rest as opposed to extended rest and refuelling as in many songbirds. Daily torpor could reduce energy costs when not in flight, minimizing the need for extended stopovers and allowing bats to potentially complete their migration at a fraction of the time and energy cost of similar sized birds.</p></div>]]></content:encoded><description>1. Some bat species make long-distance latitudinal migrations between summer and winter grounds, but because of their elusive nature, few aspects of their biology are well understood. The need for migratory stopover sites to rest and refuel, such as used by birds, has been repeatedly suggested, but not previously tested empirically in bats.2. We studied migrating silver-haired bats (Lasionycteris noctivagans) at Long Point, ON, Canada. We used digital radio-transmitters to track 30 bats using an array of five towers that effectively covered the entire region (c. 20 × 40 km). We measured stopover duration and departure direction, and documented movement patterns, foraging activity and roost sites. We measured body composition on arrival using quantitative magnetic resonance and simulated long-distance migration using observed body composition to predict migration range and rate.3. Migration occurred in two waves (late August and mid-September). Most bats stayed 1–2 days, although two remained &gt;2 weeks. One third of the bats foraged while at the site, many foraging opportunistically on nights when rain precluded continued migration. Bats roosted in a variety of tree species and manmade structures in natural and developed areas. Half of the bats departed across Lake Erie (minimum crossing distance c. 38 km) while half departed along the shoreline.4. Simulations predicted a migration rate of c. 250–275 km per day and suggest that all but one of the bats in our study carried sufficient fuel stores to reach the putative wintering area (estimated distance 1500 km) without further refuelling.5. Our results suggest that migrating bats stopover for sanctuary or short-term rest as opposed to extended rest and refuelling as in many songbirds. Daily torpor could reduce energy costs when not in flight, minimizing the need for extended stopovers and allowing bats to potentially complete their migration at a fraction of the time and energy cost of similar sized birds.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01920.x" xmlns="http://purl.org/rss/1.0/"><title>Interactions between environmental variables determine immunity in the Indian meal moth Plodia interpunctella</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01920.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Interactions between environmental variables determine immunity in the Indian meal moth Plodia interpunctella</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alison Triggs</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert J. Knell</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01920.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01920.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01920.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">386</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">394</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Animals raised in good environmental conditions are expected to have more resources to invest in immunity than those raised in poor conditions. Variation in immune activity and parasite resistance in response to changes in environmental temperature, population density and food quality have been shown in many invertebrate species.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Almost all studies to date have examined the effects of individual variables in isolation. The aim of this study was to address whether environmental factors interact to produce synergistic effects on phenoloxidase (PO) activity and haemocyte count, both indicators of immune system activity. Temperature, food quality and density were varied in a fully factorial design for a total of eight treatment combinations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Strong interactions between the three environmental variables led to the magnitude and in some cases the direction of the effect of most variables changing as the other environmental factors were altered. Overall, food quality had the most important and consistent influence, larvae raised on a good-quality diet having substantially higher PO activity in every case and substantially higher haemocyte counts in all treatments except unheated/low density.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> When food quality was good, the larvae showed ‘density-dependent prophylaxis’: raising their investment in immunity when population density is high. When food quality was poor and the temperature low, however, those larvae raised at high densities invested less in immunity.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Increased temperature is often thought to lead to increased immune reactivity in ectotherms, but we found that the effect of temperature was strongly dependent on the values of other environmental variables. PO activity increased with temperature when larvae were raised on good food or when density was high, but when food was poor and density low, a higher temperature led to reduced PO activity. A higher temperature led to higher haemocyte counts when density was high and food quality was poor, but in all other cases, the effect of increased temperature was either close to zero or somewhat negative.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Although PO activity and haemocyte count were weakly correlated across the whole data set, there were a number of treatments where the two measures responded in different ways to environmental change. Overall, effect sizes for PO activity were substantially higher than those for haemocyte count, indicating that the different components of the immune system vary in their sensitivity to environmental change.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> Predictions of the effect of environmental or population change on immunity and disease dynamics based on laboratory experiments that only investigate the effects of single variable are likely to be inaccurate or even entirely wrong.</p></div>]]></content:encoded><description>1. Animals raised in good environmental conditions are expected to have more resources to invest in immunity than those raised in poor conditions. Variation in immune activity and parasite resistance in response to changes in environmental temperature, population density and food quality have been shown in many invertebrate species.2. Almost all studies to date have examined the effects of individual variables in isolation. The aim of this study was to address whether environmental factors interact to produce synergistic effects on phenoloxidase (PO) activity and haemocyte count, both indicators of immune system activity. Temperature, food quality and density were varied in a fully factorial design for a total of eight treatment combinations.3. Strong interactions between the three environmental variables led to the magnitude and in some cases the direction of the effect of most variables changing as the other environmental factors were altered. Overall, food quality had the most important and consistent influence, larvae raised on a good-quality diet having substantially higher PO activity in every case and substantially higher haemocyte counts in all treatments except unheated/low density.4. When food quality was good, the larvae showed ‘density-dependent prophylaxis’: raising their investment in immunity when population density is high. When food quality was poor and the temperature low, however, those larvae raised at high densities invested less in immunity.5. Increased temperature is often thought to lead to increased immune reactivity in ectotherms, but we found that the effect of temperature was strongly dependent on the values of other environmental variables. PO activity increased with temperature when larvae were raised on good food or when density was high, but when food was poor and density low, a higher temperature led to reduced PO activity. A higher temperature led to higher haemocyte counts when density was high and food quality was poor, but in all other cases, the effect of increased temperature was either close to zero or somewhat negative.6. Although PO activity and haemocyte count were weakly correlated across the whole data set, there were a number of treatments where the two measures responded in different ways to environmental change. Overall, effect sizes for PO activity were substantially higher than those for haemocyte count, indicating that the different components of the immune system vary in their sensitivity to environmental change.7. Predictions of the effect of environmental or population change on immunity and disease dynamics based on laboratory experiments that only investigate the effects of single variable are likely to be inaccurate or even entirely wrong.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01924.x" xmlns="http://purl.org/rss/1.0/"><title>Effects of food ration on SMR: influence of food consumption on individual variation in metabolic rate in juvenile coho salmon (Onchorhynchus kisutch)</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01924.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of food ration on SMR: influence of food consumption on individual variation in metabolic rate in juvenile coho salmon (Onchorhynchus kisutch)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Travis E. Van Leeuwen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jordan S. Rosenfeld</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jeffrey G. Richards</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01924.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01924.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01924.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">395</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">402</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Consistency of differences in standard metabolic rate (SMR) between individual juvenile salmonids and the apparently limited ability of individuals to regulate their SMR has led many researchers to conclude that differences in individual SMR are fixed (i.e. genetic).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> To test for the effects of food ration on individual performance and metabolism, SMR was estimated by measuring oxygen consumption using flow-through respirometry on individually separated young of the year coho salmon (<em>Oncorhynchus kisutch</em>) placed on varying food rations over a period of 44 days.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Results demonstrate that the quantity of food consumed directly affects SMR of juvenile coho salmon, independent of specific dynamic action (SDA, an elevation in metabolic rate from the increased energy demands associated with digestion immediately following a meal) and indicates that higher food consumption is a cause of elevated SMR rather than a consequence of it. Juvenile coho salmon therefore demonstrated an ability to regulate their SMR according to food availability and ultimately food consumption.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> This study indicates that food consumption may play a pivotal role in understanding individual variation in SMR independent of inherent genetic differences. We suggest that studies involving SMR need to be cautious about the effects of intra-individual differences in food consumption in communal tanks or in different microhabitats in the wild as disproportionate food consumption may contribute more to variation in SMR than intrinsic (genetic) factors.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> In general, our results suggest that evolutionary changes in SMR are likely a response to selection on food consumption and growth, rather than SMR itself.</p></div>]]></content:encoded><description>1. Consistency of differences in standard metabolic rate (SMR) between individual juvenile salmonids and the apparently limited ability of individuals to regulate their SMR has led many researchers to conclude that differences in individual SMR are fixed (i.e. genetic).2. To test for the effects of food ration on individual performance and metabolism, SMR was estimated by measuring oxygen consumption using flow-through respirometry on individually separated young of the year coho salmon (Oncorhynchus kisutch) placed on varying food rations over a period of 44 days.3. Results demonstrate that the quantity of food consumed directly affects SMR of juvenile coho salmon, independent of specific dynamic action (SDA, an elevation in metabolic rate from the increased energy demands associated with digestion immediately following a meal) and indicates that higher food consumption is a cause of elevated SMR rather than a consequence of it. Juvenile coho salmon therefore demonstrated an ability to regulate their SMR according to food availability and ultimately food consumption.4. This study indicates that food consumption may play a pivotal role in understanding individual variation in SMR independent of inherent genetic differences. We suggest that studies involving SMR need to be cautious about the effects of intra-individual differences in food consumption in communal tanks or in different microhabitats in the wild as disproportionate food consumption may contribute more to variation in SMR than intrinsic (genetic) factors.5. In general, our results suggest that evolutionary changes in SMR are likely a response to selection on food consumption and growth, rather than SMR itself.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01923.x" xmlns="http://purl.org/rss/1.0/"><title>Goshawk prey have more bacteria than non-prey</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01923.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Goshawk prey have more bacteria than non-prey</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">A. P. Møller</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. M. Peralta-Sánchez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. T. Nielsen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">E. López-Hernández</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. J. Soler</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01923.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01923.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01923.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">403</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">410</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Predators often prey on individuals that are sick or otherwise weakened. Although previous studies have shown higher abundance of parasites in prey, whether prey have elevated loads of micro-organisms remains to be determined.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> We quantified the abundance of bacteria and fungi on feathers of woodpigeons <em>Columba palumbus</em> L., jays <em>Garrulus glandarius</em> L. and blackbirds <em>Turdus merula</em> L. that either fell prey to goshawks <em>Accipiter gentilis</em> L. or were not depredated.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We found an almost three-fold increase in bacterial load of prey compared with non-prey, while there was no significant difference between prey and non-prey in level of fungal infection of the plumage.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> The results were not confounded by differences in size or mass of feathers, date of collection of feathers, or date of analysis of feathers for micro-organisms.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> These findings suggest a previously unknown contribution of bacteria to risk of predation, with important implications for behaviour, population ecology and community ecology.</p></div>]]></content:encoded><description>1. Predators often prey on individuals that are sick or otherwise weakened. Although previous studies have shown higher abundance of parasites in prey, whether prey have elevated loads of micro-organisms remains to be determined.2. We quantified the abundance of bacteria and fungi on feathers of woodpigeons Columba palumbus L., jays Garrulus glandarius L. and blackbirds Turdus merula L. that either fell prey to goshawks Accipiter gentilis L. or were not depredated.3. We found an almost three-fold increase in bacterial load of prey compared with non-prey, while there was no significant difference between prey and non-prey in level of fungal infection of the plumage.4. The results were not confounded by differences in size or mass of feathers, date of collection of feathers, or date of analysis of feathers for micro-organisms.5. These findings suggest a previously unknown contribution of bacteria to risk of predation, with important implications for behaviour, population ecology and community ecology.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01919.x" xmlns="http://purl.org/rss/1.0/"><title>Fluctuations in population composition dampen the impact of phenotypic plasticity on trait dynamics in superb fairy-wrens</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01919.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Fluctuations in population composition dampen the impact of phenotypic plasticity on trait dynamics in superb fairy-wrens</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Martijn van de Pol</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Helen L. Osmond</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Andrew Cockburn</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01919.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01919.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01919.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">411</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">422</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> In structured populations, phenotypic change can result from changes throughout an individual’s lifetime (phenotypic plasticity, age-related changes), selection and changes in population composition (environment- or density-driven fluctuations in age-structure).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> The contribution of population dynamics to phenotypic change has often been ignored. However, for understanding trait dynamics, it is important to identify both the individual- and population-level mechanisms responsible for trait change, because they potentially reinforce or counteract each other.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We use 22 years of field data to investigate the dynamics of a sexually selected phenological trait, the timing of nuptial moult in superb fairy-wrens <em>Malurus cyaneus</em>.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> We show that trait expression is both climate- and age-dependent, but that phenotypic plasticity in response to climate variability also varies with age. Old males can acquire nuptial plumage very early after high rainfall, but 1- to 2-year-olds cannot. However, males of all ages that defer moult to later in the year acquire nuptial plumage earlier when conditions are warmer.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> The underlying mechanism appears to be that old males may risk moulting in the most challenging period of the year: in autumn, when drought restricts food abundance and during the cold winter. By contrast, young males always moult during the spring transition to benign – warmer and generally wetter – conditions. Temperature changes dominate this transition that heralds the breeding season, thereby causing both young and late-moulting older birds to be temperature sensitive.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>6.</b> Climate and age also affect trait dynamics via a population dynamical pathway. The same high rainfall that triggers early moulting in old males concurrently increases offspring recruitment and thereby reduces the average age of males in the population. Consequently, effects of rainfall on trait dynamics through phenotypic plasticity of old males are dampened by synchronous rejuvenation of the age-structure.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>7.</b> A long-term trend towards drier environments prompted phenotypic change because of plasticity, but this was masked by climate-driven demographic change (causing apparent stasis). This suggests a novel explanation for why trait change may fail to reflect the observed pattern of directional selection or phenotypic plasticity.</p></div>]]></content:encoded><description>1. In structured populations, phenotypic change can result from changes throughout an individual’s lifetime (phenotypic plasticity, age-related changes), selection and changes in population composition (environment- or density-driven fluctuations in age-structure).2. The contribution of population dynamics to phenotypic change has often been ignored. However, for understanding trait dynamics, it is important to identify both the individual- and population-level mechanisms responsible for trait change, because they potentially reinforce or counteract each other.3. We use 22 years of field data to investigate the dynamics of a sexually selected phenological trait, the timing of nuptial moult in superb fairy-wrens Malurus cyaneus.4. We show that trait expression is both climate- and age-dependent, but that phenotypic plasticity in response to climate variability also varies with age. Old males can acquire nuptial plumage very early after high rainfall, but 1- to 2-year-olds cannot. However, males of all ages that defer moult to later in the year acquire nuptial plumage earlier when conditions are warmer.5. The underlying mechanism appears to be that old males may risk moulting in the most challenging period of the year: in autumn, when drought restricts food abundance and during the cold winter. By contrast, young males always moult during the spring transition to benign – warmer and generally wetter – conditions. Temperature changes dominate this transition that heralds the breeding season, thereby causing both young and late-moulting older birds to be temperature sensitive.6. Climate and age also affect trait dynamics via a population dynamical pathway. The same high rainfall that triggers early moulting in old males concurrently increases offspring recruitment and thereby reduces the average age of males in the population. Consequently, effects of rainfall on trait dynamics through phenotypic plasticity of old males are dampened by synchronous rejuvenation of the age-structure.7. A long-term trend towards drier environments prompted phenotypic change because of plasticity, but this was masked by climate-driven demographic change (causing apparent stasis). This suggests a novel explanation for why trait change may fail to reflect the observed pattern of directional selection or phenotypic plasticity.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01910.x" xmlns="http://purl.org/rss/1.0/"><title>Male reproductive success increases with alliance size in Indo-Pacific bottlenose dolphins (Tursiops aduncus)</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01910.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Male reproductive success increases with alliance size in Indo-Pacific bottlenose dolphins (Tursiops aduncus)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joanna Wiszniewski</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Shannon Corrigan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luciano B. Beheregaray</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luciana M. Möller</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01910.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01910.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01910.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">423</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">431</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Determining the extent of variation in male mating strategies and reproductive success is necessary to understand the fitness benefits of social and cooperative behaviour.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> This study assesses the reproductive success of male Indo-Pacific bottlenose dolphins in a small embayment population where different behavioural strategies of males have previously been identified. Parentage for 44 sampled calves was examined using 23 microsatellite loci and one mitochondrial DNA marker. Our candidate parent pool of 70 males and 64 females contained individuals sampled from both the embayment and adjacent coastal populations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> A moderate level of polygyny was detected in our sample. We assigned paternity of 23 calves to 12 males at the strict 95% confidence level and an additional nine calves to two males at the 80% confidence level. The majority (92%) of successful males were identified as residents to the embayment, and 46% of offspring were located within the same social group or community as their father.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Our results suggest that the size of alliances was the best predictor of reproductive success for males in this population, while the strength of association among allied males, alliance stability and male ranging patterns had little influence. In line with predictions for male alliances formed between unrelated individuals, we found that reproductive skew within alliances was not large.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Together, our genetic and behavioural analyses demonstrate that alliance formation between male dolphins is a successful strategy to enhance reproductive output.</p></div>]]></content:encoded><description>1. Determining the extent of variation in male mating strategies and reproductive success is necessary to understand the fitness benefits of social and cooperative behaviour.2. This study assesses the reproductive success of male Indo-Pacific bottlenose dolphins in a small embayment population where different behavioural strategies of males have previously been identified. Parentage for 44 sampled calves was examined using 23 microsatellite loci and one mitochondrial DNA marker. Our candidate parent pool of 70 males and 64 females contained individuals sampled from both the embayment and adjacent coastal populations.3. A moderate level of polygyny was detected in our sample. We assigned paternity of 23 calves to 12 males at the strict 95% confidence level and an additional nine calves to two males at the 80% confidence level. The majority (92%) of successful males were identified as residents to the embayment, and 46% of offspring were located within the same social group or community as their father.4. Our results suggest that the size of alliances was the best predictor of reproductive success for males in this population, while the strength of association among allied males, alliance stability and male ranging patterns had little influence. In line with predictions for male alliances formed between unrelated individuals, we found that reproductive skew within alliances was not large.5. Together, our genetic and behavioural analyses demonstrate that alliance formation between male dolphins is a successful strategy to enhance reproductive output.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01914.x" xmlns="http://purl.org/rss/1.0/"><title>Lévy flight and Brownian search patterns of a free-ranging predator reflect different prey field characteristics</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01914.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Lévy flight and Brownian search patterns of a free-ranging predator reflect different prey field characteristics</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David W. Sims</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nicolas E. Humphries</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Russell W. Bradford</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Barry D. Bruce</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01914.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01914.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01914.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">432</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">442</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Search processes play an important role in physical, chemical and biological systems. In animal foraging, the search strategy predators should use to search optimally for prey is an enduring question. Some models demonstrate that when prey is sparsely distributed, an optimal search pattern is a specialised random walk known as a Lévy flight, whereas when prey is abundant, simple Brownian motion is sufficiently efficient. These predictions form part of what has been termed the Lévy flight foraging hypothesis (LFF) which states that as Lévy flights optimise random searches, movements approximated by optimal Lévy flights may have naturally evolved in organisms to enhance encounters with targets (e.g. prey) when knowledge of their locations is incomplete.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Whether free-ranging predators exhibit the movement patterns predicted in the LFF hypothesis in response to known prey types and distributions, however, has not been determined. We tested this using vertical and horizontal movement data from electronic tagging of an apex predator, the great white shark <em>Carcharodon carcharias</em>, across widely differing habitats reflecting different prey types.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> Individual white sharks exhibited movement patterns that predicted well the prey types expected under the LFF hypothesis. Shark movements were best approximated by Brownian motion when hunting near abundant, predictable sources of prey (e.g. seal colonies, fish aggregations), whereas movements approximating truncated Lévy flights were present when searching for sparsely distributed or potentially difficult-to-detect prey in oceanic or shelf environments, respectively.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> That movement patterns approximated by truncated Lévy flights and Brownian behaviour were present in the predicted prey fields indicates search strategies adopted by white sharks appear to be the most efficient ones for encountering prey in the habitats where such patterns are observed. This suggests that <em>C. carcharias</em> appears capable of exhibiting search patterns that are approximated as optimal in response to encountered changes in prey type and abundance, and across diverse marine habitats, from the surf zone to the deep ocean.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our results provide some support for the LFF hypothesis. However, it is possible that the observed Lévy patterns of white sharks may not arise from an adaptive behaviour but could be an emergent property arising from simple, straight-line movements between complex (e.g. fractal) distributions of prey. Experimental studies are needed in vertebrates to test for the presence of Lévy behaviour patterns in the absence of complex prey distributions.</p></div>]]></content:encoded><description>1. Search processes play an important role in physical, chemical and biological systems. In animal foraging, the search strategy predators should use to search optimally for prey is an enduring question. Some models demonstrate that when prey is sparsely distributed, an optimal search pattern is a specialised random walk known as a Lévy flight, whereas when prey is abundant, simple Brownian motion is sufficiently efficient. These predictions form part of what has been termed the Lévy flight foraging hypothesis (LFF) which states that as Lévy flights optimise random searches, movements approximated by optimal Lévy flights may have naturally evolved in organisms to enhance encounters with targets (e.g. prey) when knowledge of their locations is incomplete.2. Whether free-ranging predators exhibit the movement patterns predicted in the LFF hypothesis in response to known prey types and distributions, however, has not been determined. We tested this using vertical and horizontal movement data from electronic tagging of an apex predator, the great white shark Carcharodon carcharias, across widely differing habitats reflecting different prey types.3. Individual white sharks exhibited movement patterns that predicted well the prey types expected under the LFF hypothesis. Shark movements were best approximated by Brownian motion when hunting near abundant, predictable sources of prey (e.g. seal colonies, fish aggregations), whereas movements approximating truncated Lévy flights were present when searching for sparsely distributed or potentially difficult-to-detect prey in oceanic or shelf environments, respectively.4. That movement patterns approximated by truncated Lévy flights and Brownian behaviour were present in the predicted prey fields indicates search strategies adopted by white sharks appear to be the most efficient ones for encountering prey in the habitats where such patterns are observed. This suggests that C. carcharias appears capable of exhibiting search patterns that are approximated as optimal in response to encountered changes in prey type and abundance, and across diverse marine habitats, from the surf zone to the deep ocean.5. Our results provide some support for the LFF hypothesis. However, it is possible that the observed Lévy patterns of white sharks may not arise from an adaptive behaviour but could be an emergent property arising from simple, straight-line movements between complex (e.g. fractal) distributions of prey. Experimental studies are needed in vertebrates to test for the presence of Lévy behaviour patterns in the absence of complex prey distributions.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01928.x" xmlns="http://purl.org/rss/1.0/"><title>Predicting the potential demographic impact of predators on their prey: a comparative analysis of two carnivore–ungulate systems in Scandinavia</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01928.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Predicting the potential demographic impact of predators on their prey: a comparative analysis of two carnivore–ungulate systems in Scandinavia</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Vincenzo Gervasi</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Erlend B. Nilsen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Håkan Sand</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manuela Panzacchi</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Geir R. Rauset</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hans C. Pedersen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jonas Kindberg</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Petter Wabakken</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Barbara Zimmermann</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John Odden</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Olof Liberg</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jon E. Swenson</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John D. C. Linnell</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01928.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01928.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01928.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">443</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">454</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Understanding the role of predation in shaping the dynamics of animal communities is a fundamental issue in ecological research. Nevertheless, the complex nature of predator–prey interactions often prevents researchers from modelling them explicitly.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> By using periodic Leslie–Usher matrices and a simulation approach together with parameters obtained from long-term field projects, we reconstructed the underlying mechanisms of predator–prey demographic interactions and compared the dynamics of the roe deer–red fox–Eurasian lynx–human harvest system with those of the moose–brown bear–gray wolf–human harvest system in the boreal forest ecosystem of the southern Scandinavian Peninsula.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> The functional relationship of both roe deer and moose λ to changes in predation rates from the four predators was remarkably different. Lynx had the strongest impact among the four predators, whereas predation rates by wolves, red foxes, or brown bears generated minor variations in prey population λ. Elasticity values of lynx, wolf, fox and bear predation rates were −0·157, −0·056, −0·031 and −0·006, respectively, but varied with both predator and prey densities.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Differences in predation impact were only partially related to differences in kill or predation rates, but were rather a result of different distribution of predation events among prey age classes. Therefore, the age composition of killed individuals emerged as the main underlying factor determining the overall per capita impact of predation.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Our results confirm the complex nature of predator–prey interactions in large terrestrial mammals, by showing that different carnivores preying on the same prey species can exert a dramatically different demographic impact, even in the same ecological context, as a direct consequence of their predation patterns. Similar applications of this analytical framework in other geographical and ecological contexts are needed, but a more general evaluation of the subject is also required, aimed to assess, on a broader systematic and ecological range, what specific traits of a carnivore are most related to its potential impact on prey species.</p></div>]]></content:encoded><description>1. Understanding the role of predation in shaping the dynamics of animal communities is a fundamental issue in ecological research. Nevertheless, the complex nature of predator–prey interactions often prevents researchers from modelling them explicitly.2. By using periodic Leslie–Usher matrices and a simulation approach together with parameters obtained from long-term field projects, we reconstructed the underlying mechanisms of predator–prey demographic interactions and compared the dynamics of the roe deer–red fox–Eurasian lynx–human harvest system with those of the moose–brown bear–gray wolf–human harvest system in the boreal forest ecosystem of the southern Scandinavian Peninsula.3. The functional relationship of both roe deer and moose λ to changes in predation rates from the four predators was remarkably different. Lynx had the strongest impact among the four predators, whereas predation rates by wolves, red foxes, or brown bears generated minor variations in prey population λ. Elasticity values of lynx, wolf, fox and bear predation rates were −0·157, −0·056, −0·031 and −0·006, respectively, but varied with both predator and prey densities.4. Differences in predation impact were only partially related to differences in kill or predation rates, but were rather a result of different distribution of predation events among prey age classes. Therefore, the age composition of killed individuals emerged as the main underlying factor determining the overall per capita impact of predation.5. Our results confirm the complex nature of predator–prey interactions in large terrestrial mammals, by showing that different carnivores preying on the same prey species can exert a dramatically different demographic impact, even in the same ecological context, as a direct consequence of their predation patterns. Similar applications of this analytical framework in other geographical and ecological contexts are needed, but a more general evaluation of the subject is also required, aimed to assess, on a broader systematic and ecological range, what specific traits of a carnivore are most related to its potential impact on prey species.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01900.x" xmlns="http://purl.org/rss/1.0/"><title>Phylogenetic structure illuminates the mechanistic role of environmental heterogeneity in community organization</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01900.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Phylogenetic structure illuminates the mechanistic role of environmental heterogeneity in community organization</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Richard D. Stevens</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Maria M. Gavilanez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Juan S. Tello</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David A. Ray</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01900.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01900.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01900.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">455</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">462</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1. </b>Diversity begets diversity. Numerous published positive correlations between environmental heterogeneity and species diversity indicate ubiquity of this phenomenon. Nonetheless, most assessments of this relationship are phenomenological and provide little insight into the mechanism whereby such positive association results.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2. </b>Two unresolved issues could better illuminate the mechanistic basis to diversity begets diversity. First, as environmental heterogeneity increases, both productivity and the species richness that contributes to that productivity often increase in a correlated fashion thus obscuring the primary driver. Second, it is unclear how species are added to communities as diversity increases and whether additions are trait based.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3. </b>We examined these issues based on 31 rodent communities in the central Mojave Desert. At each site, we estimated rodent species richness and characterized environmental heterogeneity from the perspectives of standing primary productivity and number of seed resources. We further examined the phylogenetic structure of communities by estimating the mean phylogenetic distance (MPD) among species and by comparing empirical phylogenetic distances to those based on random assembly from a regional species pool.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4. </b>The relationship between rodent species diversity and environmental heterogeneity was positive and significant. Moreover, diversity of resources accounted for more unique variation than did total productivity, suggesting that variety and not total amount of resource was the driver of increased rodent diversity. Relationships between environmental heterogeneity and phylogenetic distance were negative and significant; species were significantly phylogenetically over-dispersed in communities of low environmental heterogeneity and became more clumped as environmental heterogeneity increased.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5. </b>Results suggest that species diversity increases with environmental heterogeneity because a wider variety of resources allow greater species packing within communities.</p></div>]]></content:encoded><description>1. Diversity begets diversity. Numerous published positive correlations between environmental heterogeneity and species diversity indicate ubiquity of this phenomenon. Nonetheless, most assessments of this relationship are phenomenological and provide little insight into the mechanism whereby such positive association results.2. Two unresolved issues could better illuminate the mechanistic basis to diversity begets diversity. First, as environmental heterogeneity increases, both productivity and the species richness that contributes to that productivity often increase in a correlated fashion thus obscuring the primary driver. Second, it is unclear how species are added to communities as diversity increases and whether additions are trait based.3. We examined these issues based on 31 rodent communities in the central Mojave Desert. At each site, we estimated rodent species richness and characterized environmental heterogeneity from the perspectives of standing primary productivity and number of seed resources. We further examined the phylogenetic structure of communities by estimating the mean phylogenetic distance (MPD) among species and by comparing empirical phylogenetic distances to those based on random assembly from a regional species pool.4. The relationship between rodent species diversity and environmental heterogeneity was positive and significant. Moreover, diversity of resources accounted for more unique variation than did total productivity, suggesting that variety and not total amount of resource was the driver of increased rodent diversity. Relationships between environmental heterogeneity and phylogenetic distance were negative and significant; species were significantly phylogenetically over-dispersed in communities of low environmental heterogeneity and became more clumped as environmental heterogeneity increased.5. Results suggest that species diversity increases with environmental heterogeneity because a wider variety of resources allow greater species packing within communities.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01921.x" xmlns="http://purl.org/rss/1.0/"><title>Patterns and processes in abundance–body size relationships for marine benthic invertebrates</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01921.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Patterns and processes in abundance–body size relationships for marine benthic invertebrates</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tsuyuko Yamanaka</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Piran C. L. White</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Matthew Spencer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dave Raffaelli</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01921.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01921.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01921.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">463</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">471</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> The nature of abundance–body size relationships in animal communities, and especially the drivers behind the observed patterns, have been a focus of persistent debate in animal ecology. In a recent review, <a href="#b2" rel="references:#b2">Allen <em>et al.</em> (2006)</a> categorized five mechanistic explanations behind the commonly observed polymodality in these relationships: energetic constraints; phylogenetic constraints; biogeographical determinants; habitat structure; and community interactions. Progress in understanding of these patterns and the processes underlying them have been hindered by the use of a range of methods that differ in their validity and robustness.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> Here, we used data on invertebrate body sizes from a variety of sandy beaches in the UK to test the hypothesis that these communities display modality in their abundance–body size relationships. We quantified modality in the relationships using kernel density estimation and smoothed bootstrap resampling and then evaluated the competing explanations for this modality based on the patterns identified in conjunction with measurements of the physical beach environment.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> We found bimodal distributions in the body size spectrum for benthic invertebrates at nine of 16 sites. There was a consistent trough in the spectrum at around 0·5–1 mm diameter, which reflected the traditional split between meiofauna and macrofauna. Beaches with finer particle sizes and more heterogeneous macrofauna hosted communities with more than two modes.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Our results suggest that modality in sandy beach benthic communities is unlikely to be explained by any single hypothesis. There will be an interplay between physical and biological factors, with different explanations accounting for modality at different scales.</p></div>]]></content:encoded><description>1. The nature of abundance–body size relationships in animal communities, and especially the drivers behind the observed patterns, have been a focus of persistent debate in animal ecology. In a recent review, Allen et al. (2006) categorized five mechanistic explanations behind the commonly observed polymodality in these relationships: energetic constraints; phylogenetic constraints; biogeographical determinants; habitat structure; and community interactions. Progress in understanding of these patterns and the processes underlying them have been hindered by the use of a range of methods that differ in their validity and robustness.2. Here, we used data on invertebrate body sizes from a variety of sandy beaches in the UK to test the hypothesis that these communities display modality in their abundance–body size relationships. We quantified modality in the relationships using kernel density estimation and smoothed bootstrap resampling and then evaluated the competing explanations for this modality based on the patterns identified in conjunction with measurements of the physical beach environment.3. We found bimodal distributions in the body size spectrum for benthic invertebrates at nine of 16 sites. There was a consistent trough in the spectrum at around 0·5–1 mm diameter, which reflected the traditional split between meiofauna and macrofauna. Beaches with finer particle sizes and more heterogeneous macrofauna hosted communities with more than two modes.4. Our results suggest that modality in sandy beach benthic communities is unlikely to be explained by any single hypothesis. There will be an interplay between physical and biological factors, with different explanations accounting for modality at different scales.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01922.x" xmlns="http://purl.org/rss/1.0/"><title>Similarity and difference among rainforest fruit-feeding butterfly communities in Central and South America</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01922.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Similarity and difference among rainforest fruit-feeding butterfly communities in Central and South America</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Philip J. DeVries</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Laura G. Alexander</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Isidro A. Chacon</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">James A. Fordyce</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01922.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01922.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01922.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">472</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">482</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Documenting species abundance distributions in natural environments is critical to ecology and conservation biology. Tropical forest insect faunas vary in space and time, and these partitions can differ in their contribution to overall species diversity.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> In the Neotropics, the Central American butterfly fauna is best known in terms of general natural history, but butterfly community diversity is best documented by studies on South American fruit-feeding butterflies. Here, we present the first long-term study of fruit-feeding nymphalid species diversity from Central America and provide a unique comparison between Central and South American butterfly communities.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> This study used 60 months of sampling among multiple spatial and temporal partitions to assess species diversity in a Costa Rican rainforest butterfly community. Abundance distributions varied significantly at the species and higher taxonomic group levels, and canopy and understorey samples were found to be composed of distinct species assemblages.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Strong similarities in patterns of species diversity were found between this study and one from Ecuador; yet, there was an important difference in how species richness was distributed in vertical space. In contrast to the Ecuadorian site, Costa Rica had significantly higher canopy richness and lower understorey richness.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> This study affirms that long-term sampling is vital to understanding tropical insect species abundance distributions and points to potential differences in vertical structure among Central and South American forest insect communities that need to be explored.</p></div>]]></content:encoded><description>1. Documenting species abundance distributions in natural environments is critical to ecology and conservation biology. Tropical forest insect faunas vary in space and time, and these partitions can differ in their contribution to overall species diversity.2. In the Neotropics, the Central American butterfly fauna is best known in terms of general natural history, but butterfly community diversity is best documented by studies on South American fruit-feeding butterflies. Here, we present the first long-term study of fruit-feeding nymphalid species diversity from Central America and provide a unique comparison between Central and South American butterfly communities.3. This study used 60 months of sampling among multiple spatial and temporal partitions to assess species diversity in a Costa Rican rainforest butterfly community. Abundance distributions varied significantly at the species and higher taxonomic group levels, and canopy and understorey samples were found to be composed of distinct species assemblages.4. Strong similarities in patterns of species diversity were found between this study and one from Ecuador; yet, there was an important difference in how species richness was distributed in vertical space. In contrast to the Ecuadorian site, Costa Rica had significantly higher canopy richness and lower understorey richness.5. This study affirms that long-term sampling is vital to understanding tropical insect species abundance distributions and points to potential differences in vertical structure among Central and South American forest insect communities that need to be explored.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01927.x" xmlns="http://purl.org/rss/1.0/"><title>Mixed competition–predation: potential vs. realized interactions</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01927.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Mixed competition–predation: potential vs. realized interactions</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lennart Persson</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">André M. De Roos</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01927.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01927.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01927.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">483</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">493</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Life-history omnivory or size-induced mixed competition–predation systems have under many conditions theoretically been shown to be fragile, whereas at the same time existing empirical data suggest such systems to be common in nature.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> In a whole lake experiment covering 17 years, we analysed the effects of the introduction of the intraguild prey roach (<em>Rutilus rutilus</em>) on the population size and individual performance of the intraguild predator perch (<em>Perca fluviatilis</em>) and on resource levels in two low productivity systems.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> A strong long-term effect of roach on the zooplankton resource but not on the macroinvertebrate resource was present. Competitive effects of roach on perch were observed in one of the lakes the first years after the introduction, but at the end of the study no competitive effect of roach on either size class of perch was observed in any of the two lakes. In contrast, a positive predatory effect reflected in improved growth rates of older perch was present.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> The lack of a support for a competitive effect of roach on small perch raises the question of the importance of mixed competition–predation interactions in life-history omnivorous systems and the problem of comparing descriptive data on feeding relationships with theoretical predictions based on interaction modules.</p></div>]]></content:encoded><description>1. Life-history omnivory or size-induced mixed competition–predation systems have under many conditions theoretically been shown to be fragile, whereas at the same time existing empirical data suggest such systems to be common in nature.2. In a whole lake experiment covering 17 years, we analysed the effects of the introduction of the intraguild prey roach (Rutilus rutilus) on the population size and individual performance of the intraguild predator perch (Perca fluviatilis) and on resource levels in two low productivity systems.3. A strong long-term effect of roach on the zooplankton resource but not on the macroinvertebrate resource was present. Competitive effects of roach on perch were observed in one of the lakes the first years after the introduction, but at the end of the study no competitive effect of roach on either size class of perch was observed in any of the two lakes. In contrast, a positive predatory effect reflected in improved growth rates of older perch was present.4. The lack of a support for a competitive effect of roach on small perch raises the question of the importance of mixed competition–predation interactions in life-history omnivorous systems and the problem of comparing descriptive data on feeding relationships with theoretical predictions based on interaction modules.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01929.x" xmlns="http://purl.org/rss/1.0/"><title>The indirect consequences of a mutualism: comparing positive and negative components of the net interaction between honeydew-tending ants and host plants</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01929.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The indirect consequences of a mutualism: comparing positive and negative components of the net interaction between honeydew-tending ants and host plants</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joshua B. Grinath</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Brian D. Inouye</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nora Underwood</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ian Billick</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01929.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01929.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01929.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">494</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">502</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>1. In ecological webs, net indirect interactions between species are composed of interactions that vary in sign and magnitude. Most studies have focused on negative component interactions (e.g. predation, herbivory) without considering the relative importance of positive interactions (e.g. mutualism, facilitation) for determining net indirect effects.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>2. In plant/arthropod communities, ants have multiple top-down effects via mutualisms with honeydew-producing herbivores and harassment of and predation on other herbivores; these ant effects provide opportunities for testing the relative importance of positive and negative interspecific interactions. We manipulated the presence of ants, honeydew-producing membracids and leaf-chewing beetles on perennial host plants in field experiments in Colorado to quantify the relative strength of these different types of interactions and their impact on the ant’s net indirect effect on plants.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>3. In 2007, we demonstrated that ants simultaneously had a positive effect on membracids and a negative effect on beetles, resulting in less beetle damage on plants hosting the mutualism.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>4. In 2008, we used structural equation modelling to describe interaction strengths through the entire insect herbivore community on plants with and without ants. The ant’s mutualism with membracids was the sole strong interaction contributing to the net indirect effect of ants on plants. Predation, herbivory and facilitation were weak, and the net effect of ants reduced plant reproduction. This net indirect effect was also partially because of behavioural changes of herbivores in the presence of ants. An additional membracid manipulation showed that the membracid’s effect on ant activity was largely responsible for the ant’s net effect on plants; ant workers were nearly ten times as abundant on plants with mutualists, and effects on other herbivores were similar to those in the ant manipulation experiment.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>5. These results demonstrate that mutualisms can be strong relative to negative direct interspecific interactions and that positive interactions deserve attention as important components of ecological webs.</p></div>]]></content:encoded><description>1. In ecological webs, net indirect interactions between species are composed of interactions that vary in sign and magnitude. Most studies have focused on negative component interactions (e.g. predation, herbivory) without considering the relative importance of positive interactions (e.g. mutualism, facilitation) for determining net indirect effects.2. In plant/arthropod communities, ants have multiple top-down effects via mutualisms with honeydew-producing herbivores and harassment of and predation on other herbivores; these ant effects provide opportunities for testing the relative importance of positive and negative interspecific interactions. We manipulated the presence of ants, honeydew-producing membracids and leaf-chewing beetles on perennial host plants in field experiments in Colorado to quantify the relative strength of these different types of interactions and their impact on the ant’s net indirect effect on plants.3. In 2007, we demonstrated that ants simultaneously had a positive effect on membracids and a negative effect on beetles, resulting in less beetle damage on plants hosting the mutualism.4. In 2008, we used structural equation modelling to describe interaction strengths through the entire insect herbivore community on plants with and without ants. The ant’s mutualism with membracids was the sole strong interaction contributing to the net indirect effect of ants on plants. Predation, herbivory and facilitation were weak, and the net effect of ants reduced plant reproduction. This net indirect effect was also partially because of behavioural changes of herbivores in the presence of ants. An additional membracid manipulation showed that the membracid’s effect on ant activity was largely responsible for the ant’s net effect on plants; ant workers were nearly ten times as abundant on plants with mutualists, and effects on other herbivores were similar to those in the ant manipulation experiment.5. These results demonstrate that mutualisms can be strong relative to negative direct interspecific interactions and that positive interactions deserve attention as important components of ecological webs.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01926.x" xmlns="http://purl.org/rss/1.0/"><title>Multi-objective behavioural mechanisms are adopted by foraging animals to achieve several optimality goals simultaneously</title><link>http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01926.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Multi-objective behavioural mechanisms are adopted by foraging animals to achieve several optimality goals simultaneously</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eric Wajnberg</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-03-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1365-2656.2011.01926.x</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/j.1365-2656.2011.01926.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1365-2656.2011.01926.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">503</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">511</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Summary</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>1.</b> Animals foraging for resources are under a variety of selective pressures, and separate optimality models have been developed predicting the optimal reproductive strategies they should adopt.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>2.</b> In most cases, the proximate behavioural mechanisms adopted to achieve such optimality goals have been identified. This is the case, for example, for optimal patch time and sex allocation in insect parasitoids. However, behaviours modelled within this framework have mainly been studied separately, even though real animals have to optimize some behaviours simultaneously.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>3.</b> For this reason, it would be better if proximate behavioural rules were designed to attain several goals simultaneously. Despite their importance, such multi-objective proximate rules remain to be discovered.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>4.</b> Based on experiments on insect parasitoids that simultaneously examine their optimal patch time and sex allocation strategies, it is shown here that animals can adopt multi-objective behavioural mechanisms that appear consistent with the two optimal goals simultaneously.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><b>5.</b> Results of computer simulations demonstrate that these behavioural mechanisms are indeed consistent with optimal reproductive strategies and have thus been most likely selected over the course of the evolutionary time.</p></div>]]></content:encoded><description>1. Animals foraging for resources are under a variety of selective pressures, and separate optimality models have been developed predicting the optimal reproductive strategies they should adopt.2. In most cases, the proximate behavioural mechanisms adopted to achieve such optimality goals have been identified. This is the case, for example, for optimal patch time and sex allocation in insect parasitoids. However, behaviours modelled within this framework have mainly been studied separately, even though real animals have to optimize some behaviours simultaneously.3. For this reason, it would be better if proximate behavioural rules were designed to attain several goals simultaneously. Despite their importance, such multi-objective proximate rules remain to be discovered.4. Based on experiments on insect parasitoids that simultaneously examine their optimal patch time and sex allocation strategies, it is shown here that animals can adopt multi-objective behavioural mechanisms that appear consistent with the two optimal goals simultaneously.5. Results of computer simulations demonstrate that these behavioural mechanisms are indeed consistent with optimal reproductive strategies and have thus been most likely selected over the course of the evolutionary time.</description></item></rdf:RDF>
