<?xml version="1.0" encoding="UTF-8"?>
<?xml-stylesheet href="http://onlinelibrarystatic.wiley.com/xslt/wol-journal-rss.xsl"
            type="text/xsl"?><rdf:RDF xmlns:rdf="http://www.w3.org/1999/02/22-rdf-syntax-ns#"><channel rdf:about="http://onlinelibrary.wiley.com/rss/journal/10.1111/(ISSN)1744-7429" xmlns="http://purl.org/rss/1.0/"><title>Biotropica</title><description> Wiley Online Library : Biotropica</description><link>http://dx.doi.org/10.1111%2F%28ISSN%291744-7429</link><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc</dc:publisher><dc:language xmlns:dc="http://purl.org/dc/elements/1.1/">en</dc:language><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/">© Association for Tropical Biology and Conservation</dc:rights><prism:issn xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">0006-3606</prism:issn><prism:eIssn xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1744-7429</prism:eIssn><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><prism:coverDisplayDate xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">January 2012</prism:coverDisplayDate><prism:volume xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">44</prism:volume><prism:number xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:number><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">138</prism:endingPage><image rdf:resource="http://onlinelibrary.wiley.com/store/10.1111/btp.2011.44.issue-1/asset/cover.gif?v=1&amp;s=8cf0e3de2bd53a39cf26ba9a07c2cca18334337d"/><items><rdf:Seq><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00859.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00858.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00856.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00860.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00855.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00852.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00851.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00850.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00843.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00847.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00841.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00846.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00842.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00845.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00833.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00840.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00839.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00838.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00837.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00835.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00836.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00825.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00830.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00832.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00828.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00827.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00834.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00821.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00822.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00824.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00831.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00816.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00819.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00820.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00799.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00812.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00814.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00813.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00815.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00809.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00803.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00796.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00794.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00795.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00801.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00797.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00791.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00789.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00788.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00786.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00784.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00785.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00783.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00781.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00779.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00782.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00780.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00823.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00818.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00771.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00767.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00773.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00763.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00777.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00765.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00776.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00775.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00768.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00774.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00772.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00766.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00769.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00770.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00848.x"/><rdf:li rdf:resource="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00849.x"/></rdf:Seq></items></channel><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00859.x" xmlns="http://purl.org/rss/1.0/"><title>Mating Behavior Drives Seed Dispersal by the Long-wattled Umbrellabird Cephalopterus penduliger</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00859.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Mating Behavior Drives Seed Dispersal by the Long-wattled Umbrellabird Cephalopterus penduliger</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jordan Karubian</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Renata Durães</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jenny L. Storey</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas B. Smith</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-10T16:28:39.614716-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2012.00859.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.1744-7429.2012.00859.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00859.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Frugivores exhibit considerable variation in the seed dispersal services they provide. Understanding what drives these differences is a key goal for ecologists because of the central role seed dispersal plays in shaping ecological and genetic diversity in plant populations. The lek-mating system of the Long-wattled Umbrellabird (<em>Cephalopterus penduliger</em>) provides a powerful lens to examine how mating behavior may impact seed dispersal outcomes. As in all lek-breeding species, male Umbrellabirds congregate in traditional sites (leks) to display, whereas females are solitary and visit leks only rarely. This study demonstrates how differences in mating behavior between the sexes drive distinctive seed movement and deposition patterns by male vs. female Umbrellabirds. Using radio tracking and gut retention trials, we documented divergent movement patterns between the sexes that are directly attributable to mating behavior differences. These movement differences led males to disperse seeds long distances from source trees and to deposit the majority of seeds they ingested within the lek; females dispersed seeds shorter distances and more evenly across the landscape. We empirically confirmed that the density of dispersed seeds was higher in leks than in control areas outside the lek, yet found no evidence that this higher density of seeds in leks reduced probability of seedling establishment. This research not only provides a mechanistic explanation for long dispersal distances and high levels of genetic diversity previously reported for seeds in Umbrellabird leks, but also highlights the importance of explicitly considering behavior in studies of animal-mediated seed dispersal.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Frugivores exhibit considerable variation in the seed dispersal services they provide. Understanding what drives these differences is a key goal for ecologists because of the central role seed dispersal plays in shaping ecological and genetic diversity in plant populations. The lek-mating system of the Long-wattled Umbrellabird (Cephalopterus penduliger) provides a powerful lens to examine how mating behavior may impact seed dispersal outcomes. As in all lek-breeding species, male Umbrellabirds congregate in traditional sites (leks) to display, whereas females are solitary and visit leks only rarely. This study demonstrates how differences in mating behavior between the sexes drive distinctive seed movement and deposition patterns by male vs. female Umbrellabirds. Using radio tracking and gut retention trials, we documented divergent movement patterns between the sexes that are directly attributable to mating behavior differences. These movement differences led males to disperse seeds long distances from source trees and to deposit the majority of seeds they ingested within the lek; females dispersed seeds shorter distances and more evenly across the landscape. We empirically confirmed that the density of dispersed seeds was higher in leks than in control areas outside the lek, yet found no evidence that this higher density of seeds in leks reduced probability of seedling establishment. This research not only provides a mechanistic explanation for long dispersal distances and high levels of genetic diversity previously reported for seeds in Umbrellabird leks, but also highlights the importance of explicitly considering behavior in studies of animal-mediated seed dispersal.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00858.x" xmlns="http://purl.org/rss/1.0/"><title>Impact of Culm Harvest on Seed Production in a Monocarpic Bamboo</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00858.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Impact of Culm Harvest on Seed Production in a Monocarpic Bamboo</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Arun Jyoti Nath</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Donald C. Franklin</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael J. Lawes</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mukta Chandra Das</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ashesh Kumar Das</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-10T16:14:40.671862-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2012.00858.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.1744-7429.2012.00858.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00858.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Successful regeneration of bamboos from seed is a key issue in the ecology of many tropical regions and the livelihoods of their inhabitants. The gregarious monocarpy of many bamboos may be driven by a need to satiate seed predators by seeding in abundance at infrequent intervals. In long-lived clonal monocarps, seed production is expected to be positively related to the success of the clone in generating more and larger ramets during its lifetime. Ramification may be constrained by harvesting of culms, but it is unclear whether the reduction in productivity is proportional to the loss of reproductive biomass. We counted the seed produced by 661 culms (ramet stems) sampled from 90 clumps of the gregariously monocarpic bamboo <em>Schizostachyum dullooa</em> that is intensively harvested by villagers in northeastern India. The smallest clumps had fewer culms and few or no culms more than one year old. Seed production was indeed positively related to culm size and the number of culms in a clump. First-year culms were markedly more productive than older culms after controlling for culm diameter and clump size. There was a negative effect of clump size on productivity per culm which may occur because clumps that had been harvested heavily were able to exploit resources retained in rhizomes from harvested culms. Nevertheless, small clumps produced much less seed than larger clumps, generating a risk of unknown magnitude that heavily harvested stands of monocarpic bamboos may be unable to satiate seed predators during their single opportunity for reproduction.</p></div>]]></content:encoded><description>Successful regeneration of bamboos from seed is a key issue in the ecology of many tropical regions and the livelihoods of their inhabitants. The gregarious monocarpy of many bamboos may be driven by a need to satiate seed predators by seeding in abundance at infrequent intervals. In long-lived clonal monocarps, seed production is expected to be positively related to the success of the clone in generating more and larger ramets during its lifetime. Ramification may be constrained by harvesting of culms, but it is unclear whether the reduction in productivity is proportional to the loss of reproductive biomass. We counted the seed produced by 661 culms (ramet stems) sampled from 90 clumps of the gregariously monocarpic bamboo Schizostachyum dullooa that is intensively harvested by villagers in northeastern India. The smallest clumps had fewer culms and few or no culms more than one year old. Seed production was indeed positively related to culm size and the number of culms in a clump. First-year culms were markedly more productive than older culms after controlling for culm diameter and clump size. There was a negative effect of clump size on productivity per culm which may occur because clumps that had been harvested heavily were able to exploit resources retained in rhizomes from harvested culms. Nevertheless, small clumps produced much less seed than larger clumps, generating a risk of unknown magnitude that heavily harvested stands of monocarpic bamboos may be unable to satiate seed predators during their single opportunity for reproduction.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00856.x" xmlns="http://purl.org/rss/1.0/"><title>The Ranging Costs of a Fallback Food: Liana Consumption Supplements Diet but Increases Foraging Effort in Howler Monkeys</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00856.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Ranging Costs of a Fallback Food: Liana Consumption Supplements Diet but Increases Foraging Effort in Howler Monkeys</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jacob C. Dunn</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Norberto Asensio</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Victor Arroyo-Rodríguez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stefan Schnitzer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jurgi Cristóbal-Azkarate</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-07T08:45:22.885874-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2012.00856.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.1744-7429.2012.00856.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00856.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Lianas are important components in the dynamics of tropical forests and represent fallback foods for some primates, yet little is known about their impact on primate ecology, behavior or fitness. Using 2 yr of field data, we investigated liana consumption and foraging effort in four groups of howler monkeys (two in bigger, more conserved forest fragments and two in smaller, less conserved fragments) to assess whether howler monkeys use lianas when and where food availability is scarce, and how liana consumption is related to foraging effort. Howler monkeys in smaller fragments spent more time consuming lianas and liana consumption was negatively related to the consumption of preferred food resources (fruit and <em>Ficus</em> spp.). Further, travel time was positively related to liana feeding time, but not to tree feeding time, and howler monkeys visited a greater number of food patches when feeding from liana leaves than when feeding from tree leaves. Our results suggest that these increases in foraging effort were related to the fact that lianas are mainly a source of leaves, and that liana patch size was probably smaller than tree patch size. While these results were clear when analyzing all four groups combined, however, they were not always significant in each of the groups individually. We suggest that this may be related to the differences in group size, patch size and the availability of resources among groups. Further studies are necessary to assess whether these dietary and behavioral adjustments negatively impact on the fitness and conservation of primates in fragments.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Lianas are important components in the dynamics of tropical forests and represent fallback foods for some primates, yet little is known about their impact on primate ecology, behavior or fitness. Using 2 yr of field data, we investigated liana consumption and foraging effort in four groups of howler monkeys (two in bigger, more conserved forest fragments and two in smaller, less conserved fragments) to assess whether howler monkeys use lianas when and where food availability is scarce, and how liana consumption is related to foraging effort. Howler monkeys in smaller fragments spent more time consuming lianas and liana consumption was negatively related to the consumption of preferred food resources (fruit and Ficus spp.). Further, travel time was positively related to liana feeding time, but not to tree feeding time, and howler monkeys visited a greater number of food patches when feeding from liana leaves than when feeding from tree leaves. Our results suggest that these increases in foraging effort were related to the fact that lianas are mainly a source of leaves, and that liana patch size was probably smaller than tree patch size. While these results were clear when analyzing all four groups combined, however, they were not always significant in each of the groups individually. We suggest that this may be related to the differences in group size, patch size and the availability of resources among groups. Further studies are necessary to assess whether these dietary and behavioral adjustments negatively impact on the fitness and conservation of primates in fragments.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00860.x" xmlns="http://purl.org/rss/1.0/"><title>Effects of Local Plant Density and Incomplete Dichogamy on the Reproductive Success of the Rare Neotropical Palm Geonoma epetiolata</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00860.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of Local Plant Density and Incomplete Dichogamy on the Reproductive Success of the Rare Neotropical Palm Geonoma epetiolata</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Silvana Martén-Rodríguez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mauricio Quesada</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Braham Momen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-07T08:44:48.46039-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2012.00860.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.1744-7429.2012.00860.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00860.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Density dependent processes are known to influence reproduction and establishment of plant populations. In this study, we evaluated the effects of local density and sexual expression on the reproductive success of the rare palm species <em>Geonoma epetiolata</em> in Costa Rica. We classified individuals in two density categories based on distances to the two nearest neighbors and recorded the occurrence of sexual overlap on each individual. Overlap between pistillate and staminate flowers in monoecious plants allows geitonogamous pollination, potentially reducing dependence on mates for reproduction. We measured plant size and light availability, and evaluated the influence of these variables on pollination success, fruit production, fruit abortion and seed mass. Pollination success significantly increased with density but there was no effect of sexual overlap. In contrast, there was no effect of density on the probability of initiated fruit, and a negative effect on fruit set. Fruit abortion was lowest in isolated plants with no sexual overlap. Plant size and light did not contribute to variation in reproductive success. In conclusion, the pollination advantage of plants in dense neighborhoods does not compensate reproductive losses incurred by fruit abortion, possibly due to mating among genetically related individuals. <em>Geonoma epetiolata</em> is threatened by habitat loss and poaching of seeds for the horticultural market. High fruit abortion rates associated with density in <em>G. epetiolata</em> suggest that seed collections from the remnant wild populations of this palm species may cause bottlenecks that further threaten population viability.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Density dependent processes are known to influence reproduction and establishment of plant populations. In this study, we evaluated the effects of local density and sexual expression on the reproductive success of the rare palm species Geonoma epetiolata in Costa Rica. We classified individuals in two density categories based on distances to the two nearest neighbors and recorded the occurrence of sexual overlap on each individual. Overlap between pistillate and staminate flowers in monoecious plants allows geitonogamous pollination, potentially reducing dependence on mates for reproduction. We measured plant size and light availability, and evaluated the influence of these variables on pollination success, fruit production, fruit abortion and seed mass. Pollination success significantly increased with density but there was no effect of sexual overlap. In contrast, there was no effect of density on the probability of initiated fruit, and a negative effect on fruit set. Fruit abortion was lowest in isolated plants with no sexual overlap. Plant size and light did not contribute to variation in reproductive success. In conclusion, the pollination advantage of plants in dense neighborhoods does not compensate reproductive losses incurred by fruit abortion, possibly due to mating among genetically related individuals. Geonoma epetiolata is threatened by habitat loss and poaching of seeds for the horticultural market. High fruit abortion rates associated with density in G. epetiolata suggest that seed collections from the remnant wild populations of this palm species may cause bottlenecks that further threaten population viability.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00855.x" xmlns="http://purl.org/rss/1.0/"><title>Effects of Treefall Gap Disturbances on Ant Assemblages in a Tropical Montane Cloud Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00855.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of Treefall Gap Disturbances on Ant Assemblages in a Tropical Montane Cloud Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Margaret Patrick</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David Fowler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert R. Dunn</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nathan J. Sanders</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-02T09:50:09.035627-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2012.00855.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.1744-7429.2012.00855.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2012.00855.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The study of gap dynamics and the effects of gaps on diversity has been at the center of tropical ecology for decades. While most studies have focused on the responses of plant species and communities to gap formation, in this study, we consider the effects of treefall gap disturbances on leaf litter ant assemblages in a Neotropical montane cloud forest. We sampled leaf litter ant assemblages and estimated a suite of abiotic parameters in 12 large (&gt;80-m<sup>2</sup>) treefall gaps across a chronosequence and in 12 paired adjacent intact forest sites in the Monteverde Cloud Forest Preserve in Costa Rica. No species were more common in gaps than in intact forests, and in fact, species that were common in gaps were also among the most common in forests. The Chao2 estimate of species richness, however, was higher in gap sites than in intact forest sites. In addition, ant assemblages in gap sites did not become more similar to those in adjacent intact sites as gaps aged. In contrast to other studies, our work demonstrates that ant assemblages in the Monteverde Cloud Forest Preserve are weakly affected by the formation of treefall gaps. Together, these results indicate that treefall gap dynamics probably play little role in promoting ant diversity at more regional scales, or coexistence among species at more local scales.</p></div>]]></content:encoded><description>The study of gap dynamics and the effects of gaps on diversity has been at the center of tropical ecology for decades. While most studies have focused on the responses of plant species and communities to gap formation, in this study, we consider the effects of treefall gap disturbances on leaf litter ant assemblages in a Neotropical montane cloud forest. We sampled leaf litter ant assemblages and estimated a suite of abiotic parameters in 12 large (&gt;80-m2) treefall gaps across a chronosequence and in 12 paired adjacent intact forest sites in the Monteverde Cloud Forest Preserve in Costa Rica. No species were more common in gaps than in intact forests, and in fact, species that were common in gaps were also among the most common in forests. The Chao2 estimate of species richness, however, was higher in gap sites than in intact forest sites. In addition, ant assemblages in gap sites did not become more similar to those in adjacent intact sites as gaps aged. In contrast to other studies, our work demonstrates that ant assemblages in the Monteverde Cloud Forest Preserve are weakly affected by the formation of treefall gaps. Together, these results indicate that treefall gap dynamics probably play little role in promoting ant diversity at more regional scales, or coexistence among species at more local scales.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00852.x" xmlns="http://purl.org/rss/1.0/"><title>A Revised Conservation Assessment of Dipterocarps in Sabah</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00852.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">A Revised Conservation Assessment of Dipterocarps in Sabah</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Colin R. Maycock</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Chris J. Kettle</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eyen Khoo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joan T. Pereira</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John B. Sugau</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Reuben Nilus</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert C. Ong</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nazahatul A. Amaludin</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mark F. Newman</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David F.R.P. Burslem</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-23T06:31:29.394273-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00852.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.1744-7429.2011.00852.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00852.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Borneo has experienced a rapid decline in the extent of forest cover, which has reduced the amount of habitat available for many plant and animal species. The precise impact of habitat loss on the conservation status of dipterocarp trees is uncertain. We use three contrasting techniques, the extent of occurrence, area of occupancy and ecological niche models derived using <span class="smallCaps">maxent</span>, in conjunction with a current land-use map of Sabah, to derive estimates of habitat loss and infer a regional IUCN Red List conservation status for 33 Sabah dipterocarp species. Estimates of habitat loss differed significantly according to the methods employed and between species on different habitat types. Proportion of habitat loss determined from the ecological niche models varied from 21 percent for <em>Shorea micans</em> to 99.5 percent for <em>Dipterocarpus lamellatus</em>. Thirty-two of the 33 dipterocarp species analyzed in this study would have their Sabah populations classified as Threatened (equal to a habitat loss of &gt; 30%) under the A2 IUCN Red List criterion. Dipterocarps that occur in lowland forests have experienced greater habitat loss than upland/lower montane or ultramafic species. In addition, species with the lowest predicted area within their historic distributions had the highest proportion of habitat lost, which provides a rationale for targeting conservation effort on the species with narrow distributions. We recommend the ecological niche modeling approach as a rapid assessment tool for reconstructing species’ historic distributions during conservation assessments of tropical trees.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Malay is available in the online version of this article.</p></div>]]></content:encoded><description>Borneo has experienced a rapid decline in the extent of forest cover, which has reduced the amount of habitat available for many plant and animal species. The precise impact of habitat loss on the conservation status of dipterocarp trees is uncertain. We use three contrasting techniques, the extent of occurrence, area of occupancy and ecological niche models derived using maxent, in conjunction with a current land-use map of Sabah, to derive estimates of habitat loss and infer a regional IUCN Red List conservation status for 33 Sabah dipterocarp species. Estimates of habitat loss differed significantly according to the methods employed and between species on different habitat types. Proportion of habitat loss determined from the ecological niche models varied from 21 percent for Shorea micans to 99.5 percent for Dipterocarpus lamellatus. Thirty-two of the 33 dipterocarp species analyzed in this study would have their Sabah populations classified as Threatened (equal to a habitat loss of &gt; 30%) under the A2 IUCN Red List criterion. Dipterocarps that occur in lowland forests have experienced greater habitat loss than upland/lower montane or ultramafic species. In addition, species with the lowest predicted area within their historic distributions had the highest proportion of habitat lost, which provides a rationale for targeting conservation effort on the species with narrow distributions. We recommend the ecological niche modeling approach as a rapid assessment tool for reconstructing species’ historic distributions during conservation assessments of tropical trees.Abstract in Malay is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00851.x" xmlns="http://purl.org/rss/1.0/"><title>Avian Composition Co-varies with Floristic Composition and Soil Nutrient Concentration in Amazonian Upland Forests</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00851.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Avian Composition Co-varies with Floristic Composition and Soil Nutrient Concentration in Amazonian Upland Forests</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lars Y. Pomara</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kalle Ruokolainen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hanna Tuomisto</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kenneth R. Young</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-19T00:07:35.298261-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00851.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.1744-7429.2011.00851.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00851.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Spatial heterogeneity in the plant species composition of tropical forests is expected to influence animal species abundance and composition because vegetation constitutes the primary habitat feature for forest animals. Floristic variation is tied to variation in soils, so edaphic properties should ultimately influence animal species composition as well. The study of covariation in floristic and faunistic turnover has been hindered by the difficulty of completing coordinated surveys in hyperdiverse tropical communities, but this can be overcome with the use of a few plant taxa that function as surrogates for general floristic turnover. We used avian and plant transect surveys and soil sampling in a western Amazonian upland (<em>terra firme</em>) forest landscape to test whether spatial variation in bird community composition is associated with floristic turnover and corresponding edaphic gradients. Partial Mantel tests and Non-metric Multidimensional Scaling showed floristic distinctiveness between two forest types closely associated with differences in soil cation concentrations, and differences in both floristic composition and cation concentrations were further linked to compositional differences in avian species, independent of geographic distances among sites. Ten percent of bird species included in Indicator Species Analyses showed significant associations with one of the two forest types. The upland forest types that we sampled, each corresponding to a different geological formation, are intermediate relative to edaphically extreme environments in the region. Models of avian diversification should take into account this environmental heterogeneity, as should conservation planning approaches that aim to represent faunal diversity.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Spatial heterogeneity in the plant species composition of tropical forests is expected to influence animal species abundance and composition because vegetation constitutes the primary habitat feature for forest animals. Floristic variation is tied to variation in soils, so edaphic properties should ultimately influence animal species composition as well. The study of covariation in floristic and faunistic turnover has been hindered by the difficulty of completing coordinated surveys in hyperdiverse tropical communities, but this can be overcome with the use of a few plant taxa that function as surrogates for general floristic turnover. We used avian and plant transect surveys and soil sampling in a western Amazonian upland (terra firme) forest landscape to test whether spatial variation in bird community composition is associated with floristic turnover and corresponding edaphic gradients. Partial Mantel tests and Non-metric Multidimensional Scaling showed floristic distinctiveness between two forest types closely associated with differences in soil cation concentrations, and differences in both floristic composition and cation concentrations were further linked to compositional differences in avian species, independent of geographic distances among sites. Ten percent of bird species included in Indicator Species Analyses showed significant associations with one of the two forest types. The upland forest types that we sampled, each corresponding to a different geological formation, are intermediate relative to edaphically extreme environments in the region. Models of avian diversification should take into account this environmental heterogeneity, as should conservation planning approaches that aim to represent faunal diversity.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00850.x" xmlns="http://purl.org/rss/1.0/"><title>Emergent Impacts of Ant and Spider Interactions: Herbivory Reduction in a Tropical Savanna Tree</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00850.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Emergent Impacts of Ant and Spider Interactions: Herbivory Reduction in a Tropical Savanna Tree</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Larissa Nahas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marcelo O. Gonzaga</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kleber Del-Claro</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-17T05:14:14.828779-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00850.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.1744-7429.2011.00850.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00850.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Multiple predators often have effects on their common prey populations that cannot be predicted by summing the effects of each predator at a time. When predators forage on the same vegetation substrate, intraguild interactions might cause emergent outcomes for the plants on which the predators co-occur. We experimentally evaluated the effects of spiders and ants on herbivory and reproduction in the extrafloral nectary-bearing tree <em>Qualea multiflora</em> (Vochysiaceae). Plants were divided in four experimental groups, depending on the presence or absence of ants and spiders. We compared the effects of each treatment on richness and abundance of chewing and sucking herbivores and on herbivory (leaf area loss). We also evaluated the impact of predators on the production of buds, fruits and seeds, and weight of the fruits. The presence of ants reduced the abundance and richness of spiders, but spiders did not affect the abundance and richness of ants. Only the removal of ants resulted in a significant increase in the abundance of herbivores and herbivore richness. Herbivory, however, was also affected by spiders. In addition, we found a significant interaction effect of ants and spiders on herbivory, indicating an emergent multiple predator effect. Neither ants nor spiders had an impact on the number of buds produced, number of fruits per bud, and seeds per fruits or fruit weight. This study highlights the importance of evaluating the effect of the predator fauna as a whole and not only one specific group on herbivory.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>Multiple predators often have effects on their common prey populations that cannot be predicted by summing the effects of each predator at a time. When predators forage on the same vegetation substrate, intraguild interactions might cause emergent outcomes for the plants on which the predators co-occur. We experimentally evaluated the effects of spiders and ants on herbivory and reproduction in the extrafloral nectary-bearing tree Qualea multiflora (Vochysiaceae). Plants were divided in four experimental groups, depending on the presence or absence of ants and spiders. We compared the effects of each treatment on richness and abundance of chewing and sucking herbivores and on herbivory (leaf area loss). We also evaluated the impact of predators on the production of buds, fruits and seeds, and weight of the fruits. The presence of ants reduced the abundance and richness of spiders, but spiders did not affect the abundance and richness of ants. Only the removal of ants resulted in a significant increase in the abundance of herbivores and herbivore richness. Herbivory, however, was also affected by spiders. In addition, we found a significant interaction effect of ants and spiders on herbivory, indicating an emergent multiple predator effect. Neither ants nor spiders had an impact on the number of buds produced, number of fruits per bud, and seeds per fruits or fruit weight. This study highlights the importance of evaluating the effect of the predator fauna as a whole and not only one specific group on herbivory.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00843.x" xmlns="http://purl.org/rss/1.0/"><title>Continuous and Fluctuating Leaf Phenology of Adults and Seedlings of a Shade-tolerant Emergent Tree, Dipterocarpus sublamellatus, in Malaysia</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00843.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Continuous and Fluctuating Leaf Phenology of Adults and Seedlings of a Shade-tolerant Emergent Tree, Dipterocarpus sublamellatus, in Malaysia</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Noriyuki Osada</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Naoko Tokuchi</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hiroshi Takeda</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-12T00:40:18.148805-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00843.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.1744-7429.2011.00843.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00843.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Continuous leaf phenology, with sequential production of metamers, is usually found in pioneer species, but is rare in shade-tolerant species. Because of the nature of ‘continuous’ growth, continuous phenology has seldom been related to meteorological factors. We studied the leaf demography of seedlings and tall trees of a shade-tolerant emergent species, <em>Dipterocarpus sublamellatus</em> (Dipterocarpaceae), in Malaysia. Although leaf phenology of <em>D. sublamellatus</em> was classified as continuous, the rates of leaf production and leaf fall were not constant and greatly fluctuated during the census period. Seasonal patterns of leaf production and fall were not synchronized across tall trees in most combinations or between seedlings and tall trees. Mean number of leaves produced per month and its seasonal fluctuation were greater in tall trees than in seedlings. Moreover, relationships between leaf phenology and meteorological factors (monthly rainfall, net radiation, maximum and minimum temperature, and minimum relative humidity) differed among trees. This suggests that endogenous rhythms, <em>i.e</em>., differences in allocation of resources to growth and storage among trees, are important to fluctuations in leaf phenology. These patterns are in contrast to patterns found in various pioneer species with continuous phenology, in which rates of leaf production and fall are generally constant. Different patterns might be caused by differences in allocation to growth and storage between pioneer and shade-tolerant species, and might be related to their regeneration strategies.</p></div>]]></content:encoded><description>Continuous leaf phenology, with sequential production of metamers, is usually found in pioneer species, but is rare in shade-tolerant species. Because of the nature of ‘continuous’ growth, continuous phenology has seldom been related to meteorological factors. We studied the leaf demography of seedlings and tall trees of a shade-tolerant emergent species, Dipterocarpus sublamellatus (Dipterocarpaceae), in Malaysia. Although leaf phenology of D. sublamellatus was classified as continuous, the rates of leaf production and leaf fall were not constant and greatly fluctuated during the census period. Seasonal patterns of leaf production and fall were not synchronized across tall trees in most combinations or between seedlings and tall trees. Mean number of leaves produced per month and its seasonal fluctuation were greater in tall trees than in seedlings. Moreover, relationships between leaf phenology and meteorological factors (monthly rainfall, net radiation, maximum and minimum temperature, and minimum relative humidity) differed among trees. This suggests that endogenous rhythms, i.e., differences in allocation of resources to growth and storage among trees, are important to fluctuations in leaf phenology. These patterns are in contrast to patterns found in various pioneer species with continuous phenology, in which rates of leaf production and fall are generally constant. Different patterns might be caused by differences in allocation to growth and storage between pioneer and shade-tolerant species, and might be related to their regeneration strategies.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00847.x" xmlns="http://purl.org/rss/1.0/"><title>The Influence of Habitat, Season, and Detectability on Abundance Estimates across an Amazonian Parrot Assemblage</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00847.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Influence of Habitat, Season, and Detectability on Abundance Estimates across an Amazonian Parrot Assemblage</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alan T. K. Lee</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stuart J. Marsden</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-10T23:57:57.998343-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00847.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.1744-7429.2011.00847.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00847.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The Amazon basin holds very high parrot species richness but almost nothing is known of parrot population densities in the region or how these vary between species, habitats, sites, and seasons. Such data are becoming important as humans impact on increasing areas of the region. Seventeen parrot species were surveyed using a line transect distance sampling method over 3 yr in floodplain and <em>terra firme</em> forests at two sites in the Tambopata region of southeast Peru. Density estimates for most species were in the range of 3.3–7.8/km<sup>2</sup>, with <em>Brotogeris cyanoptera</em> and <em>Amazona farinosa</em> reaching densities of 22 and 23/km<sup>2</sup> in floodplain forest during the dry season. Parrot densities were higher in floodplain forest than in <em>terra firme</em> forest at both sites. The parrot communities of <em>terra firme</em> forests were similar across sites and seasons, but those in floodplain forests differed widely across sites and across seasons. Upper canopy birds are notoriously difficult to survey. We introduce a procedure to correct for the likely violation of the assumption that all birds on the transect line are detected (distance sampling assumption g(0) = 1). We correct g(0) based on calling rates of birds using a cue-counting technique. Multipliers for g(0) differ across species and site, but not season. This method yielded density estimates on average 22 percent higher (6–40% higher in individual species) than those from the standard method.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>The Amazon basin holds very high parrot species richness but almost nothing is known of parrot population densities in the region or how these vary between species, habitats, sites, and seasons. Such data are becoming important as humans impact on increasing areas of the region. Seventeen parrot species were surveyed using a line transect distance sampling method over 3 yr in floodplain and terra firme forests at two sites in the Tambopata region of southeast Peru. Density estimates for most species were in the range of 3.3–7.8/km2, with Brotogeris cyanoptera and Amazona farinosa reaching densities of 22 and 23/km2 in floodplain forest during the dry season. Parrot densities were higher in floodplain forest than in terra firme forest at both sites. The parrot communities of terra firme forests were similar across sites and seasons, but those in floodplain forests differed widely across sites and across seasons. Upper canopy birds are notoriously difficult to survey. We introduce a procedure to correct for the likely violation of the assumption that all birds on the transect line are detected (distance sampling assumption g(0) = 1). We correct g(0) based on calling rates of birds using a cue-counting technique. Multipliers for g(0) differ across species and site, but not season. This method yielded density estimates on average 22 percent higher (6–40% higher in individual species) than those from the standard method.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00841.x" xmlns="http://purl.org/rss/1.0/"><title>Vegetation Recovery 16 Years after Feral Pig Removal from a Wet Hawaiian Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00841.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Vegetation Recovery 16 Years after Feral Pig Removal from a Wet Hawaiian Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rebecca J. Cole</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Creighton M. Litton</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael J. Koontz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rhonda K. Loh</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-05T02:17:27.51174-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00841.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.1744-7429.2011.00841.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00841.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Nonnative ungulates can alter the structure and function of forest ecosystems. Feral pigs in particular pose a substantial threat to native plant communities throughout their global range. Hawaiian forests are exceptionally vulnerable to feral pig activity because native vegetation evolved in the absence of large mammalian herbivores. A common approach for conserving and restoring forests in Hawaii is fencing and removal of feral pigs. The extent of native plant community recovery and nonnative plant invasion following pig removal, however, is largely unknown. Our objective was to quantify changes in native and nonnative understory vegetation over a 16 yr period in adjacent fenced (pig-free) vs. unfenced (pig-present) Hawaiian montane wet forest. Native and nonnative understory vegetation responded strongly to feral pig removal. Density of native woody plants rooted in mineral soil increased sixfold in pig-free sites over 16 yr, whereas establishment was almost exclusively restricted to epiphytes in pig-present sites. Stem density of young tree ferns increased significantly (51.2%) in pig-free, but not pig-present sites. Herbaceous cover decreased over time in pig-present sites (67.9%). In both treatments, number of species remained constant and native woody plant establishment was limited to commonly occurring species. The nonnative invasive shrub, <em>Psidium cattleianum</em>, responded positively to release from pig disturbance with a fivefold increase in density in pig-free sites. These results suggest that while common native understory plants recover within 16 yr of pig removal, control of nonnative plants and outplanting of rarer native species are necessary components of sustainable conservation and restoration efforts in these forests.</p></div>]]></content:encoded><description>Nonnative ungulates can alter the structure and function of forest ecosystems. Feral pigs in particular pose a substantial threat to native plant communities throughout their global range. Hawaiian forests are exceptionally vulnerable to feral pig activity because native vegetation evolved in the absence of large mammalian herbivores. A common approach for conserving and restoring forests in Hawaii is fencing and removal of feral pigs. The extent of native plant community recovery and nonnative plant invasion following pig removal, however, is largely unknown. Our objective was to quantify changes in native and nonnative understory vegetation over a 16 yr period in adjacent fenced (pig-free) vs. unfenced (pig-present) Hawaiian montane wet forest. Native and nonnative understory vegetation responded strongly to feral pig removal. Density of native woody plants rooted in mineral soil increased sixfold in pig-free sites over 16 yr, whereas establishment was almost exclusively restricted to epiphytes in pig-present sites. Stem density of young tree ferns increased significantly (51.2%) in pig-free, but not pig-present sites. Herbaceous cover decreased over time in pig-present sites (67.9%). In both treatments, number of species remained constant and native woody plant establishment was limited to commonly occurring species. The nonnative invasive shrub, Psidium cattleianum, responded positively to release from pig disturbance with a fivefold increase in density in pig-free sites. These results suggest that while common native understory plants recover within 16 yr of pig removal, control of nonnative plants and outplanting of rarer native species are necessary components of sustainable conservation and restoration efforts in these forests.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00846.x" xmlns="http://purl.org/rss/1.0/"><title>Studying Large Mammals With Imperfect Detection: Status and Habitat Preferences of Wild Cattle and Large Carnivores in Eastern Cambodia</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00846.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Studying Large Mammals With Imperfect Detection: Status and Habitat Preferences of Wild Cattle and Large Carnivores in Eastern Cambodia</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Thomas N. E. Gray</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-05T01:56:43.488594-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00846.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.1744-7429.2011.00846.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00846.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Studying large mammal species in tropical forests is a conservation challenge with species’ behavior and ecology often increasing the probability of non-detection during surveys. Consequently, knowledge of the distribution, status, and natural history of many large mammal species in Southeast Asia is limited. I developed occupancy models from camera-trapping data, thereby accounting for imperfect detection at sampling sites, to clarify the status and habitat requirements of four globally threatened or near threatened large mammals (banteng <em>Bos javanicus</em>, gaur <em>Bos gaurus</em>, dhole <em>Cuon alpinus</em>, and leopard <em>Panthera pardus</em>) in Mondulkiri Protected Forest, eastern Cambodia. Camera traps were operational for &gt;3500 trap nights with 202 photographic encounters of the four study species. Model averaged occupancy estimates were between 5 percent (leopard) and 140 percent (gaur) higher than naive estimates (<em>i.e</em>., proportion of camera-trap sites species recorded from) thus highlighting the importance of accounting for detectability during conservation surveys. I recommend the use of an occupancy framework when using camera-trap data to study the status, ecology, and habitat preferences of poorly known and elusive species. The results highlight the importance of mixed deciduous and semi-evergreen forest for wild cattle in eastern Cambodia and I emphasize that these habitats must be considered in conservation planning across the Lower Mekong Dry Forest Ecoregion.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Khmer is available in the online version of this article.</p></div>]]></content:encoded><description>Studying large mammal species in tropical forests is a conservation challenge with species’ behavior and ecology often increasing the probability of non-detection during surveys. Consequently, knowledge of the distribution, status, and natural history of many large mammal species in Southeast Asia is limited. I developed occupancy models from camera-trapping data, thereby accounting for imperfect detection at sampling sites, to clarify the status and habitat requirements of four globally threatened or near threatened large mammals (banteng Bos javanicus, gaur Bos gaurus, dhole Cuon alpinus, and leopard Panthera pardus) in Mondulkiri Protected Forest, eastern Cambodia. Camera traps were operational for &gt;3500 trap nights with 202 photographic encounters of the four study species. Model averaged occupancy estimates were between 5 percent (leopard) and 140 percent (gaur) higher than naive estimates (i.e., proportion of camera-trap sites species recorded from) thus highlighting the importance of accounting for detectability during conservation surveys. I recommend the use of an occupancy framework when using camera-trap data to study the status, ecology, and habitat preferences of poorly known and elusive species. The results highlight the importance of mixed deciduous and semi-evergreen forest for wild cattle in eastern Cambodia and I emphasize that these habitats must be considered in conservation planning across the Lower Mekong Dry Forest Ecoregion.Abstract in Khmer is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00842.x" xmlns="http://purl.org/rss/1.0/"><title>Conservation Implications of Rapid Shifts in the Trade of Wild African and Asian Pythons</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00842.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Conservation Implications of Rapid Shifts in the Trade of Wild African and Asian Pythons</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luca Luiselli</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Xavier Bonnet</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Massimiliano Rocco</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Giovanni Amori</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-30T09:25:24.102565-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00842.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.1744-7429.2011.00842.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00842.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Pythons are harvested for the international leather industry and pet trade. We analyzed the CITES export records (1999–2008) of the most intensively commercialized wild pythons (<em>Python regius</em>,<em>Python sebae</em>,<em>Python reticulatus</em>,<em>Python molurus</em>,<em>Python curtus</em> species complex) from African and Asian countries where reliable data on trade rates and ecology are available. Mean declared annual numbers of exported pythons were 30,000 in five African countries and 164,000 in Indonesia. Trade intensity tripled in Indonesia over the last decade, but declined in Africa. African international trade is exclusively associated with the pet market (mainly United States and Europe), whereas Asian pythons are sold mostly for luxury leather, albeit more recently also for the pet trade. A negative correlation between the annual numbers of pythons traded in Africa vs. Asia suggests a rapid and recent shift of the pressure exerted on wild populations in the two main exporting continents. We also found a strong effect of the currency exchange rate (<em>i.e</em>., U.S.$/€, the currencies used by the major importing countries) on African python exports: when the cost per African python increased, importers relied increasingly on Asian providers for pet trade. Overall, our data indicate that Asian pythons (especially <em>P. reticulatus</em>) might be threatened due to the rapidly increasing pressure, whereas the decreasing international trade in African pythons is likely more sustainable.</p></div>]]></content:encoded><description>Pythons are harvested for the international leather industry and pet trade. We analyzed the CITES export records (1999–2008) of the most intensively commercialized wild pythons (Python regius,Python sebae,Python reticulatus,Python molurus,Python curtus species complex) from African and Asian countries where reliable data on trade rates and ecology are available. Mean declared annual numbers of exported pythons were 30,000 in five African countries and 164,000 in Indonesia. Trade intensity tripled in Indonesia over the last decade, but declined in Africa. African international trade is exclusively associated with the pet market (mainly United States and Europe), whereas Asian pythons are sold mostly for luxury leather, albeit more recently also for the pet trade. A negative correlation between the annual numbers of pythons traded in Africa vs. Asia suggests a rapid and recent shift of the pressure exerted on wild populations in the two main exporting continents. We also found a strong effect of the currency exchange rate (i.e., U.S.$/€, the currencies used by the major importing countries) on African python exports: when the cost per African python increased, importers relied increasingly on Asian providers for pet trade. Overall, our data indicate that Asian pythons (especially P. reticulatus) might be threatened due to the rapidly increasing pressure, whereas the decreasing international trade in African pythons is likely more sustainable.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00845.x" xmlns="http://purl.org/rss/1.0/"><title>Ecology and Hybridization Potential of Two Sympatric Metallophytes, the Narrow Endemic Crepidorhopalon perennis (Linderniaceae) and its More Widespread Congener C. tenuis</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00845.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Ecology and Hybridization Potential of Two Sympatric Metallophytes, the Narrow Endemic Crepidorhopalon perennis (Linderniaceae) and its More Widespread Congener C. tenuis</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michel-Pierre Faucon</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Benedict M. Tshilong</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fabienne Rossum</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pierre Meerts</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Guillaume Decocq</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Grégory Mahy</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-30T09:24:49.067927-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00845.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.1744-7429.2011.00845.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00845.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><em>Crepidorhopalon perennis</em> is a metallophyte critically endangered by mining activities and currently known from only one site on copper-rich soils in Katanga (Dem. Rep. Congo). It is closely related to the annual <em>C. tenuis</em>, also a rare metallophyte, but with a broader geographical range. We investigated the variation in morphometric traits and ecological niches (based on edaphic conditions and pollinator assemblages) of <em>C. perennis</em> and <em>C. tenuis</em>, to evaluate the risk of inter-specific competition, and their potential for hybridization to ascertain if <em>C. perennis</em> might be at risk of genetic swamping by its more widespread congener. We examined whether species were found under sympatric or parapatric settings with opportunity for hybridization (or gene exchange). Such knowledge is essential for implementing restoration management protocols, including the introduction of <em>C. perennis</em> into substitution sites where <em>C. tenuis</em> might be already present. Fourteen morphological characters and 11 soil variables were measured and visiting pollinator species were identified at the site where the two species co-occur. Our results show that the two species can be distinguished based on their morphological traits, show niche overlap based on edaphic properties, and share the same pollinator assemblage. In addition, no morphologically intermediate individuals could be detected, suggesting no hybridization, and that the two species may be reproductively isolated. We conclude that <em>C. perennis</em> conservation and restoration operations can be realized in substitution sites where <em>C. tenuis</em> may be present, with the need, however, to evaluate the potential effect of sharing a pollinator assemblage on reproductive success of both species.</p></div>]]></content:encoded><description>Crepidorhopalon perennis is a metallophyte critically endangered by mining activities and currently known from only one site on copper-rich soils in Katanga (Dem. Rep. Congo). It is closely related to the annual C. tenuis, also a rare metallophyte, but with a broader geographical range. We investigated the variation in morphometric traits and ecological niches (based on edaphic conditions and pollinator assemblages) of C. perennis and C. tenuis, to evaluate the risk of inter-specific competition, and their potential for hybridization to ascertain if C. perennis might be at risk of genetic swamping by its more widespread congener. We examined whether species were found under sympatric or parapatric settings with opportunity for hybridization (or gene exchange). Such knowledge is essential for implementing restoration management protocols, including the introduction of C. perennis into substitution sites where C. tenuis might be already present. Fourteen morphological characters and 11 soil variables were measured and visiting pollinator species were identified at the site where the two species co-occur. Our results show that the two species can be distinguished based on their morphological traits, show niche overlap based on edaphic properties, and share the same pollinator assemblage. In addition, no morphologically intermediate individuals could be detected, suggesting no hybridization, and that the two species may be reproductively isolated. We conclude that C. perennis conservation and restoration operations can be realized in substitution sites where C. tenuis may be present, with the need, however, to evaluate the potential effect of sharing a pollinator assemblage on reproductive success of both species.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00833.x" xmlns="http://purl.org/rss/1.0/"><title>Light-based Regeneration Niches: Evidence from 21 Dipterocarp Species using Size-specific RGRs</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00833.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Light-based Regeneration Niches: Evidence from 21 Dipterocarp Species using Size-specific RGRs</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christopher D. Philipson</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Philippe Saner</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Toby R. Marthews</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Reuben Nilus</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Glen Reynolds</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lindsay A. Turnbull</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Andy Hector</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-05T05:52:07.262433-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00833.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.1744-7429.2011.00833.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00833.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>A continuing challenge in tropical ecology is to explain the coexistence of large numbers of rain forest tree species. One possible coexistence mechanism is partitioning of the highly variable and dynamic forest light environment, in which species that grow better in one light treatment grow worse in another. To test whether species respond differently to the light environment, we estimated growth rates of 21 Dipterocarpaceae species from Malaysian Borneo grown in shade houses for 2 yr in three light treatments (0.3%, 3%, and 18% full sunlight). We made regular measurements of height, diameter, and aboveground biomass, enabling us to calculate growth rates for each response. We estimated size-specific growth rates using nonlinear mixed-effects models, as average relative growth rate was strongly size dependent. For all species, the greatest diameter growth rate was achieved in 18 percent full sunlight, whereas for five of the twenty-one species, the greatest height growth rate was achieved in three percent full sunlight. We investigated correlations among growth rates in different light treatments, but no negative correlations were found, indicating that species growing well in one light treatment did not grow poorly in the others. There were substantial crossovers, however, in species ranks among the three light treatments, indicating that there was no single growth rate hierarchy common to all light treatments. The lack of a single consistent growth hierarchy across light treatments indicates that heterogeneity in the forest light environment could contribute to the maintenance of the diversity of Dipterocarpaceae found in lowland Bornean rain forests via light-based regeneration niches.</p></div>]]></content:encoded><description>A continuing challenge in tropical ecology is to explain the coexistence of large numbers of rain forest tree species. One possible coexistence mechanism is partitioning of the highly variable and dynamic forest light environment, in which species that grow better in one light treatment grow worse in another. To test whether species respond differently to the light environment, we estimated growth rates of 21 Dipterocarpaceae species from Malaysian Borneo grown in shade houses for 2 yr in three light treatments (0.3%, 3%, and 18% full sunlight). We made regular measurements of height, diameter, and aboveground biomass, enabling us to calculate growth rates for each response. We estimated size-specific growth rates using nonlinear mixed-effects models, as average relative growth rate was strongly size dependent. For all species, the greatest diameter growth rate was achieved in 18 percent full sunlight, whereas for five of the twenty-one species, the greatest height growth rate was achieved in three percent full sunlight. We investigated correlations among growth rates in different light treatments, but no negative correlations were found, indicating that species growing well in one light treatment did not grow poorly in the others. There were substantial crossovers, however, in species ranks among the three light treatments, indicating that there was no single growth rate hierarchy common to all light treatments. The lack of a single consistent growth hierarchy across light treatments indicates that heterogeneity in the forest light environment could contribute to the maintenance of the diversity of Dipterocarpaceae found in lowland Bornean rain forests via light-based regeneration niches.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00840.x" xmlns="http://purl.org/rss/1.0/"><title>Hydrologic Connectivity Affects Fish Assemblage Structure, Diversity, and Ecological Traits in the Unregulated Gambia River, West Africa</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00840.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Hydrologic Connectivity Affects Fish Assemblage Structure, Diversity, and Ecological Traits in the Unregulated Gambia River, West Africa</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Seth M. White</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Markéta Ondračková</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Martin Reichard</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-01T01:56:13.387088-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00840.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.1744-7429.2011.00840.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00840.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The Gambia River of West Africa is a large unobstructed river, characterized by a natural flow regime and lateral connectivity across its floodplain. Construction of a major dam, however, is planned. We compared patterns of fish diversity, habitat use, assemblage structure, and the distribution of trophic position and body morphology in riverine and floodplain habitats in Niokolo Koba National Park, located downstream of the planned dam site. A total of 49 fish species were captured, revealing a lognormal distribution as expected for species-rich assemblages. Fish species exhibited a range of habitat use patterns, from generalist to highly habitat-specific, and appeared to migrate laterally among habitats between seasons. Species richness was homogenous among habitats in the wet season yet appeared to increase with isolation from the main river in the dry season. Fish assemblage structure was best explained by the interaction between habitat type and season, underlining the importance of the natural flow regime and lateral connectivity among floodplain habitats. The abundance of fishes having elongate bodies increased with isolation from the main channel in the wet season only. The distribution of fishes having compressed cross-sectional morphology decreased with isolation from the main channel in the dry season only. These patterns of trait distribution support the conclusion that variation in hydrologic connectivity structures the fish assemblage. Our results suggest that altered flow regimes and loss of floodplain habitats after damming could lead to both decreased taxonomic and functional diversity of the fish assemblage.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in French is available in the online version of this article.</p></div>]]></content:encoded><description>The Gambia River of West Africa is a large unobstructed river, characterized by a natural flow regime and lateral connectivity across its floodplain. Construction of a major dam, however, is planned. We compared patterns of fish diversity, habitat use, assemblage structure, and the distribution of trophic position and body morphology in riverine and floodplain habitats in Niokolo Koba National Park, located downstream of the planned dam site. A total of 49 fish species were captured, revealing a lognormal distribution as expected for species-rich assemblages. Fish species exhibited a range of habitat use patterns, from generalist to highly habitat-specific, and appeared to migrate laterally among habitats between seasons. Species richness was homogenous among habitats in the wet season yet appeared to increase with isolation from the main river in the dry season. Fish assemblage structure was best explained by the interaction between habitat type and season, underlining the importance of the natural flow regime and lateral connectivity among floodplain habitats. The abundance of fishes having elongate bodies increased with isolation from the main channel in the wet season only. The distribution of fishes having compressed cross-sectional morphology decreased with isolation from the main channel in the dry season only. These patterns of trait distribution support the conclusion that variation in hydrologic connectivity structures the fish assemblage. Our results suggest that altered flow regimes and loss of floodplain habitats after damming could lead to both decreased taxonomic and functional diversity of the fish assemblage.Abstract in French is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00839.x" xmlns="http://purl.org/rss/1.0/"><title>Air-breathing Behavior of the Jeju Fish Hoplerythrinus unitaeniatus in Amazonian Streams</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00839.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Air-breathing Behavior of the Jeju Fish Hoplerythrinus unitaeniatus in Amazonian Streams</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">João Alves Lima Filho</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jhany Martins</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rafael Arruda</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lucélia Nobre Carvalho</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-25T06:20:34.480965-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00839.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.1744-7429.2011.00839.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00839.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The breathing behavior of the jeju fish <em>H</em><em>oplerythrinus unitaeniatus</em> has been the focus of several studies in recent decades. Few of these studies, however, have described how the fish's air breathing functions in natural environments. We examined changes in the behavior of <em>H</em><em>. unitaeniatus</em> during daily variations in the dissolved-oxygen (DO) content of the water in Amazonian streams. We recorded the mean time intervals between instances when the fish breached the water surface to take in atmospheric air and the variation in the DO concentrations. We also observed the number of individual fish that breached the surface together as well as their territory-forming behavior. We recorded the individual and collective anti-predator strategies in the presence of a potential predator, experimentally testing the capacity of <em>H</em><em>. unitaeniatus</em> to recognize the shape of a predator. The results indicated that as the DO concentration decreased, the individuals of <em>H</em><em>. unitaeniatus</em> tended to breach the water surface at shorter time intervals, which increased their exposure to predators. To minimize the risks from this longer exposure time, the species tends to adopt anti-predator strategies individually or as a group. In well-lit locations, the fish recognized the predator's silhouette, left their territory and took a longer time to return. We provide an original contribution to the understanding of the anti-predatory tactics of the species by describing the behavior of group formation and territory definition as a tool to maximize efficiency in the defense against predators, a behavior that until now was an unknown strategy for this species.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>The breathing behavior of the jeju fish Hoplerythrinus unitaeniatus has been the focus of several studies in recent decades. Few of these studies, however, have described how the fish's air breathing functions in natural environments. We examined changes in the behavior of H. unitaeniatus during daily variations in the dissolved-oxygen (DO) content of the water in Amazonian streams. We recorded the mean time intervals between instances when the fish breached the water surface to take in atmospheric air and the variation in the DO concentrations. We also observed the number of individual fish that breached the surface together as well as their territory-forming behavior. We recorded the individual and collective anti-predator strategies in the presence of a potential predator, experimentally testing the capacity of H. unitaeniatus to recognize the shape of a predator. The results indicated that as the DO concentration decreased, the individuals of H. unitaeniatus tended to breach the water surface at shorter time intervals, which increased their exposure to predators. To minimize the risks from this longer exposure time, the species tends to adopt anti-predator strategies individually or as a group. In well-lit locations, the fish recognized the predator's silhouette, left their territory and took a longer time to return. We provide an original contribution to the understanding of the anti-predatory tactics of the species by describing the behavior of group formation and territory definition as a tool to maximize efficiency in the defense against predators, a behavior that until now was an unknown strategy for this species.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00838.x" xmlns="http://purl.org/rss/1.0/"><title>Frugivory and Seed Dispersal by Brown Lemurs in a Malagasy Tropical Dry Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00838.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Frugivory and Seed Dispersal by Brown Lemurs in a Malagasy Tropical Dry Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hiroki Sato</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-24T05:57:15.529762-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00838.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.1744-7429.2011.00838.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00838.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>In the Ankarafantsika tropical dry forest (northwestern Madagascar), the common brown lemur (<em>E</em><em>ulemur fulvus fulvus</em>) is the largest frugivore and probably the sole disperser of large-seeded plants (seed diameter &gt; 10 mm). To investigate seed dispersal by this primate, I recorded the feeding activities of a troop; also conducted fecal analyses, germination trials on defecated seeds, and a vegetation survey over 1 yr (beginning Dec 2006). Brown lemurs mostly consumed fruit (68%). The fruit of <em>V</em><em>itex beraviensis</em> was the most exploited resource (21% of total feeding time). Among dung samples, 1126 contained intact seeds of 70 plant species, with a median of six seeds and two species per sample. These data indicate that the brown lemur population dispersed approximately 9854 seeds/km<sup>2</sup>/d. Although the number of annually defecated seeds was overwhelmingly the largest in <em>G</em><em>rewia triflora</em>, many of the small seeds were often clumped in dung piles. In contrast, large seeds of <em>V</em><em>. beraviensis</em> occurred in the largest number of dung samples. The rate and time of seed germination in <em>V</em><em>. beraviensis</em> were improved by passage through brown lemur guts. Therefore, <em>V</em><em>. beraviensis</em> may readily establish seedlings in sites of brown lemur fecal deposition. <em>V</em><em>itex beraviensis</em> and brown lemurs are probably involved in a strong mutualism. Twenty-three large-seeded plants were probably dependent on brown lemurs for seed dispersal and some of these species were common trees in the forest. Maintenance of these key plant–animal interactions will probably contribute to the conservation of species diversity and intact regeneration of the Ankarafantsika forest.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in French is available in the online version of this article.</p></div>]]></content:encoded><description>In the Ankarafantsika tropical dry forest (northwestern Madagascar), the common brown lemur (Eulemur fulvus fulvus) is the largest frugivore and probably the sole disperser of large-seeded plants (seed diameter &gt; 10 mm). To investigate seed dispersal by this primate, I recorded the feeding activities of a troop; also conducted fecal analyses, germination trials on defecated seeds, and a vegetation survey over 1 yr (beginning Dec 2006). Brown lemurs mostly consumed fruit (68%). The fruit of Vitex beraviensis was the most exploited resource (21% of total feeding time). Among dung samples, 1126 contained intact seeds of 70 plant species, with a median of six seeds and two species per sample. These data indicate that the brown lemur population dispersed approximately 9854 seeds/km2/d. Although the number of annually defecated seeds was overwhelmingly the largest in Grewia triflora, many of the small seeds were often clumped in dung piles. In contrast, large seeds of V. beraviensis occurred in the largest number of dung samples. The rate and time of seed germination in V. beraviensis were improved by passage through brown lemur guts. Therefore, V. beraviensis may readily establish seedlings in sites of brown lemur fecal deposition. Vitex beraviensis and brown lemurs are probably involved in a strong mutualism. Twenty-three large-seeded plants were probably dependent on brown lemurs for seed dispersal and some of these species were common trees in the forest. Maintenance of these key plant–animal interactions will probably contribute to the conservation of species diversity and intact regeneration of the Ankarafantsika forest.Abstract in French is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00837.x" xmlns="http://purl.org/rss/1.0/"><title>Habitat Associations and Community Structure of Dipterocarps in Response to Environment and Soil Conditions in Brunei Darussalam, Northwest Borneo</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00837.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Habitat Associations and Community Structure of Dipterocarps in Response to Environment and Soil Conditions in Brunei Darussalam, Northwest Borneo</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rahayu S. Sukri</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rodzay A. Wahab</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kamariah A. Salim</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David F.R.P. Burslem</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-24T05:56:57.217686-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00837.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.1744-7429.2011.00837.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00837.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Plant habitat associations are well documented in Bornean lowland tropical forests, but few studies contrast the prevalence of associations across sites. We examined habitat associations and community composition of Dipterocarpaceae trees in two contrasting Bornean lowland mixed dipterocarp forests separated by approximately 100 km: Andulau (uniform topography, lower altitudinal range, sandy soils) and Belalong (highly dissected topography, higher altitudinal range, clay-rich soils). Dipterocarpaceae trees ≥ 1 cm diameter at breast height (dbh) were censused in 20-m wide belt transects established along topographic gradients at each site. Dipterocarp density, evenness, species richness, and diversity were significantly higher at Andulau than Belalong. Significant site associations (with either Andulau or Belalong) were detected for 19 (52%) of the 37 dipterocarp species tested. Dipterocarpaceae community composition at Belalong correlated with soil nutrient concentrations as well as measures of vegetation and topographic structure, but community composition at Andulau correlated with fewer habitat variables. Within each site, dipterocarp density, species richness, and diversity were consistently higher on ridges than in slopes and valleys. Significant within-site associations to topographic habitats were less common at Andulau (10% of species tested) than at Belalong (15%). We conclude that edaphic and other environmental factors influence dipterocarp community composition at a local scale, and are more important drivers of community structure in the more variable environment at Belalong. Species richness and diversity of dipterocarps on small plots, however, were higher at Andulau, suggesting that factors other than environmental heterogeneity contribute to contrasts in dipterocarp tree species richness at small scales.</p></div>]]></content:encoded><description>Plant habitat associations are well documented in Bornean lowland tropical forests, but few studies contrast the prevalence of associations across sites. We examined habitat associations and community composition of Dipterocarpaceae trees in two contrasting Bornean lowland mixed dipterocarp forests separated by approximately 100 km: Andulau (uniform topography, lower altitudinal range, sandy soils) and Belalong (highly dissected topography, higher altitudinal range, clay-rich soils). Dipterocarpaceae trees ≥ 1 cm diameter at breast height (dbh) were censused in 20-m wide belt transects established along topographic gradients at each site. Dipterocarp density, evenness, species richness, and diversity were significantly higher at Andulau than Belalong. Significant site associations (with either Andulau or Belalong) were detected for 19 (52%) of the 37 dipterocarp species tested. Dipterocarpaceae community composition at Belalong correlated with soil nutrient concentrations as well as measures of vegetation and topographic structure, but community composition at Andulau correlated with fewer habitat variables. Within each site, dipterocarp density, species richness, and diversity were consistently higher on ridges than in slopes and valleys. Significant within-site associations to topographic habitats were less common at Andulau (10% of species tested) than at Belalong (15%). We conclude that edaphic and other environmental factors influence dipterocarp community composition at a local scale, and are more important drivers of community structure in the more variable environment at Belalong. Species richness and diversity of dipterocarps on small plots, however, were higher at Andulau, suggesting that factors other than environmental heterogeneity contribute to contrasts in dipterocarp tree species richness at small scales.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00835.x" xmlns="http://purl.org/rss/1.0/"><title>The ‘Island Rule’ Acting on Anuran Populations (Bufonidae: Rhinella ornata) of the Southern Hemisphere</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00835.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The ‘Island Rule’ Acting on Anuran Populations (Bufonidae: Rhinella ornata) of the Southern Hemisphere</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rachel Montesinos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hélio Ricardo Silva</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">André Luiz Gomes Carvalho</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-22T06:46:42.860149-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00835.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.1744-7429.2011.00835.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00835.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Darwin and Wallace, in the mid-nineteenth century, were the first to document examples of natural selection acting on island dwellers. A century later a pattern of morphological differences among organisms on islands was coined the ‘island rule’, which states that on islands species with small individuals tend toward gigantism and large individuals tend toward dwarfism. Selective pressures such as limited resources and increased intraspecific competition modulate the size of organisms in these environments. Of the several works that have tested vertebrates for adherence to the island rule only two have addressed amphibians. This work is the third record of body size variation of island amphibian populations, and the first for the Southern Hemisphere. The islands investigated were once continuous with mainland, and now are isolated as a result of sea level fluctuations that took place in the Pleistocene and Holocene. This study compared morphometric variation in populations of <em>Rhinella ornata</em> (Bufonidae) occurring on three islands of the Costa Verde to populations on five continental areas in Rio de Janeiro, Brazil. We measured 18 morphometric variables of 177 individuals. There was a shift toward smaller body size (dwarfism) in two of the three island populations studied. We attribute this general pattern to geographic factors, verifying the expression of the island rule in tropical frogs populations (insular dwarfism) operating inversely in relation to those of temperate environments (island gigantism).</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>Darwin and Wallace, in the mid-nineteenth century, were the first to document examples of natural selection acting on island dwellers. A century later a pattern of morphological differences among organisms on islands was coined the ‘island rule’, which states that on islands species with small individuals tend toward gigantism and large individuals tend toward dwarfism. Selective pressures such as limited resources and increased intraspecific competition modulate the size of organisms in these environments. Of the several works that have tested vertebrates for adherence to the island rule only two have addressed amphibians. This work is the third record of body size variation of island amphibian populations, and the first for the Southern Hemisphere. The islands investigated were once continuous with mainland, and now are isolated as a result of sea level fluctuations that took place in the Pleistocene and Holocene. This study compared morphometric variation in populations of Rhinella ornata (Bufonidae) occurring on three islands of the Costa Verde to populations on five continental areas in Rio de Janeiro, Brazil. We measured 18 morphometric variables of 177 individuals. There was a shift toward smaller body size (dwarfism) in two of the three island populations studied. We attribute this general pattern to geographic factors, verifying the expression of the island rule in tropical frogs populations (insular dwarfism) operating inversely in relation to those of temperate environments (island gigantism).Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00836.x" xmlns="http://purl.org/rss/1.0/"><title>Fine-scale Spatial Genetic Structure of Ten Dipterocarp Tree Species in a Bornean Rain Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00836.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Fine-scale Spatial Genetic Structure of Ten Dipterocarp Tree Species in a Bornean Rain Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tsuyoshi Harata</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Satoshi Nanami</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Takuo Yamakura</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Shuhei Matsuyama</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lucy Chong</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bibian M. Diway</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sylvester Tan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Akira Itoh</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-21T04:58:15.187957-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00836.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.1744-7429.2011.00836.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00836.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Fine-scale spatial genetic structure is increasingly recognized as an important factor in the studies of tropical forest trees as it influences genetic diversity of local populations. The biologic mechanisms that generate fine-scale spatial genetic structure are not fully understood. We studied fine-scale spatial genetic structure in ten coexisting dipterocarp tree species in a Bornean rain forest using microsatellite markers. Six of the ten species showed statistically significant fine-scale spatial genetic structure. Fine-scale spatial genetic structure was stronger at smaller spatial scales (≤ 100 m) than at larger spatial scales (&gt; 100 m) for each species. Multiple regression analysis suggested that seed dispersal distance was important at the smaller spatial scale. At the larger scale (&gt; 100 m) and over the entire sample range (0–1000 m), pollinators and spatial distribution of adult trees were more important determinants of fine-scale spatial genetic structure. Fine-scale spatial genetic structure was stronger in species pollinated by less mobile small beetles than in species pollinated by the more mobile giant honeybee (<em>Apis dorsata</em>). It was also stronger in species where adult tree distributions were more clumped. The hypothesized mechanisms underlying the negative correlation between clump size and fine-scale spatial genetic structure were a large overlap among seed shadows and genetic drift within clumped species.</p></div>]]></content:encoded><description>Fine-scale spatial genetic structure is increasingly recognized as an important factor in the studies of tropical forest trees as it influences genetic diversity of local populations. The biologic mechanisms that generate fine-scale spatial genetic structure are not fully understood. We studied fine-scale spatial genetic structure in ten coexisting dipterocarp tree species in a Bornean rain forest using microsatellite markers. Six of the ten species showed statistically significant fine-scale spatial genetic structure. Fine-scale spatial genetic structure was stronger at smaller spatial scales (≤ 100 m) than at larger spatial scales (&gt; 100 m) for each species. Multiple regression analysis suggested that seed dispersal distance was important at the smaller spatial scale. At the larger scale (&gt; 100 m) and over the entire sample range (0–1000 m), pollinators and spatial distribution of adult trees were more important determinants of fine-scale spatial genetic structure. Fine-scale spatial genetic structure was stronger in species pollinated by less mobile small beetles than in species pollinated by the more mobile giant honeybee (Apis dorsata). It was also stronger in species where adult tree distributions were more clumped. The hypothesized mechanisms underlying the negative correlation between clump size and fine-scale spatial genetic structure were a large overlap among seed shadows and genetic drift within clumped species.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00825.x" xmlns="http://purl.org/rss/1.0/"><title>The Impact of Annual and Seasonal Rainfall Patterns on Growth and Phenology of Emergent Tree Species in Southeastern Amazonia, Brazil</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00825.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Impact of Annual and Seasonal Rainfall Patterns on Growth and Phenology of Emergent Tree Species in Southeastern Amazonia, Brazil</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">James Grogan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mark Schulze</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-18T05:34:07.297141-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00825.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.1744-7429.2011.00825.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00825.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Understanding tree growth in response to rainfall distribution is critical to predicting forest and species population responses to climate change. We investigated inter-annual and seasonal variation in stem diameter by three emergent tree species in a seasonally dry tropical forest in southeast Pará, Brazil. Annual diameter growth rates by <em>Swietenia macrophylla</em> demonstrated strong positive correlation with annual rainfall totals during 1997–2009; <em>Hymenaea courbaril</em> growth rates demonstrated weak positive correlation, whereas <em>Parkia pendula</em> exhibited weak negative correlation. For both <em>Swietenia</em> and <em>Hymenaea</em>, annual diameter growth rates correlated positively and significantly with rainfall totals during the first 6 mo of the growing year (July to December). Vernier dendrometer bands monitored at 4-wk intervals during 3–5 yr confirmed strong seasonal effects on stem diameter expansion. Individuals of all three species expanded in unison during wet season months and were static or even contracted during dry season months. Stems of the deciduous <em>Swietenia</em> contracted as crowns were shed during the early dry season, expanded slightly as new crowns were flushed, and then contracted further during 3–5 wk flowering periods in the late dry season by newly mature crowns. The three species’ physiographic distribution patterns at the study site may partially underlie observed differences in annual and seasonal growth. With most global circulation models predicting conditions becoming gradually drier in southeast Amazonia over the coming decades, species such as <em>Swietenia</em> that perform best on the ‘wet end’ of current conditions may experience reduced growth rates. However, population viability will not necessarily be threatened if life history and ecophysiological responses to changing conditions are compensatory.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>Understanding tree growth in response to rainfall distribution is critical to predicting forest and species population responses to climate change. We investigated inter-annual and seasonal variation in stem diameter by three emergent tree species in a seasonally dry tropical forest in southeast Pará, Brazil. Annual diameter growth rates by Swietenia macrophylla demonstrated strong positive correlation with annual rainfall totals during 1997–2009; Hymenaea courbaril growth rates demonstrated weak positive correlation, whereas Parkia pendula exhibited weak negative correlation. For both Swietenia and Hymenaea, annual diameter growth rates correlated positively and significantly with rainfall totals during the first 6 mo of the growing year (July to December). Vernier dendrometer bands monitored at 4-wk intervals during 3–5 yr confirmed strong seasonal effects on stem diameter expansion. Individuals of all three species expanded in unison during wet season months and were static or even contracted during dry season months. Stems of the deciduous Swietenia contracted as crowns were shed during the early dry season, expanded slightly as new crowns were flushed, and then contracted further during 3–5 wk flowering periods in the late dry season by newly mature crowns. The three species’ physiographic distribution patterns at the study site may partially underlie observed differences in annual and seasonal growth. With most global circulation models predicting conditions becoming gradually drier in southeast Amazonia over the coming decades, species such as Swietenia that perform best on the ‘wet end’ of current conditions may experience reduced growth rates. However, population viability will not necessarily be threatened if life history and ecophysiological responses to changing conditions are compensatory.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00830.x" xmlns="http://purl.org/rss/1.0/"><title>High Turnover Rates in Remnant Populations of the Harlequin Frog Atelopus cruciger (Bufonidae): Low Risk of Extinction?</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00830.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">High Turnover Rates in Remnant Populations of the Harlequin Frog Atelopus cruciger (Bufonidae): Low Risk of Extinction?</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Margarita Lampo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Señaris J. Celsa</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Argelia Rodríguez-Contreras</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fernando Rojas-Runjaic</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carmen Z. García</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-15T06:02:06.124047-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00830.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.1744-7429.2011.00830.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00830.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Paper</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p><em>Atelopus</em> is among the most threatened of all amphibian genera. Most species of harlequin frogs disappeared more than two decades ago and only a few still exist. From ten critically endangered <em>Atelopus</em> species endemic to Venezuela, <em>Atelopus cruciger</em> is the only one that can be located at present. To assess the status of remnant populations of <em>A. cruciger</em> and to provide the demographic data for designing <em>in situ</em> management programs, we estimated: (1) the population size; (2) the apparent survival; and (3) the recruitment rates of one remnant population using mark-recapture data. The adult population size varied (69–117), and this variation was not related to that of abundance indices based on visual counts at the river margins. Thus, caution is recommended when using visual counts as an index of abundance in <em>Atelopus</em>, because capture rates differ significantly among months and between seasons. Despite the observed variations, this population appears to be stable. Previous reports suggest that species of <em>Atelopus</em> are long-lived. For populations of long-lived species to remain approximately constant, recruitment must be low. Our mark-recapture study, however, showed that adults tend to remain in the population for approximately 15 mo, but an average of 165 new frogs are recruited every year. Although immigration and emigration are possibilities, the site fidelity and the absence of nearby streams suggests that movement in and out of the study area is less important than births and deaths. Under the proposed hypothesis of a short life expectancy/high recruitment, the risk of extinction must be lower than previously thought.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Atelopus is among the most threatened of all amphibian genera. Most species of harlequin frogs disappeared more than two decades ago and only a few still exist. From ten critically endangered Atelopus species endemic to Venezuela, Atelopus cruciger is the only one that can be located at present. To assess the status of remnant populations of A. cruciger and to provide the demographic data for designing in situ management programs, we estimated: (1) the population size; (2) the apparent survival; and (3) the recruitment rates of one remnant population using mark-recapture data. The adult population size varied (69–117), and this variation was not related to that of abundance indices based on visual counts at the river margins. Thus, caution is recommended when using visual counts as an index of abundance in Atelopus, because capture rates differ significantly among months and between seasons. Despite the observed variations, this population appears to be stable. Previous reports suggest that species of Atelopus are long-lived. For populations of long-lived species to remain approximately constant, recruitment must be low. Our mark-recapture study, however, showed that adults tend to remain in the population for approximately 15 mo, but an average of 165 new frogs are recruited every year. Although immigration and emigration are possibilities, the site fidelity and the absence of nearby streams suggests that movement in and out of the study area is less important than births and deaths. Under the proposed hypothesis of a short life expectancy/high recruitment, the risk of extinction must be lower than previously thought.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00832.x" xmlns="http://purl.org/rss/1.0/"><title>Survival and Growth of Juvenile Bromeliads in Coffee Plantations and Forests in Central Veracruz, Mexico</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00832.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Survival and Growth of Juvenile Bromeliads in Coffee Plantations and Forests in Central Veracruz, Mexico</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Susanne Scheffknecht</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manuela Winkler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Martín Mata-Rosas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Peter Hietz</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-14T08:44:19.169961-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00832.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.1744-7429.2011.00832.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00832.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Shade coffee plantations can be important refuges for epiphytes, but are not suitable for all species. To test if the performance of early life stages, often the most sensitive phase, is responsible for the species’ ability to colonize coffee plantations, we compared growth and mortality rates of three epiphytic bromeliad species that differ in their ability to colonize secondary arboreal vegetation by transplanting juveniles to trees in forests, and shade trees in old and young coffee plantations in Central Veracruz, Mexico. Growth rates of <em>T</em><em>illandsia viridiflora</em>, generally restricted to forests, and <em>Tillandsia</em><em>juncea</em>, an early colonizer, were related to the pattern of the species occurrence among habitats with growth rates of <em>T</em><em>. viridiflora</em> being generally higher in forests and growth of <em>T</em><em>. juncea</em> higher in coffee plantations. Performance of the third species, <em>Tillandsia</em><em>heterophylla</em>, which is intermediate in habitat preference, was not clearly related to habitat. No difference in growth rates was found between plants transplanted in wet or dry season. In general, mortality in transplanted bromeliads was relatively low (mostly &lt; 5% per month). In coffee plantations herbivory had a severe effect during part of the wet season, when mortality in young coffee plantations reached between 15 and 24 percent per month. Given the substantial contribution of herbivory to the mortality of juvenile plants and the significant differences between habitats, herbivory may be co-limiting the colonization of young coffee plantations by some epiphytic bromeliads.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Shade coffee plantations can be important refuges for epiphytes, but are not suitable for all species. To test if the performance of early life stages, often the most sensitive phase, is responsible for the species’ ability to colonize coffee plantations, we compared growth and mortality rates of three epiphytic bromeliad species that differ in their ability to colonize secondary arboreal vegetation by transplanting juveniles to trees in forests, and shade trees in old and young coffee plantations in Central Veracruz, Mexico. Growth rates of Tillandsia viridiflora, generally restricted to forests, and Tillandsiajuncea, an early colonizer, were related to the pattern of the species occurrence among habitats with growth rates of T. viridiflora being generally higher in forests and growth of T. juncea higher in coffee plantations. Performance of the third species, Tillandsiaheterophylla, which is intermediate in habitat preference, was not clearly related to habitat. No difference in growth rates was found between plants transplanted in wet or dry season. In general, mortality in transplanted bromeliads was relatively low (mostly &lt; 5% per month). In coffee plantations herbivory had a severe effect during part of the wet season, when mortality in young coffee plantations reached between 15 and 24 percent per month. Given the substantial contribution of herbivory to the mortality of juvenile plants and the significant differences between habitats, herbivory may be co-limiting the colonization of young coffee plantations by some epiphytic bromeliads.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00828.x" xmlns="http://purl.org/rss/1.0/"><title>Conflict between Fishermen and Giant Otters Pteronura brasiliensis in Western Brazilian Amazon</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00828.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Conflict between Fishermen and Giant Otters Pteronura brasiliensis in Western Brazilian Amazon</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Patrícia F. Rosas-Ribeiro</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fernando C.W. Rosas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jansen Zuanon</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-14T08:44:13.915643-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00828.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.1744-7429.2011.00828.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00828.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The recovery of giant otter populations after the hunting prohibition and restriction of the pelt trade resulted in more frequent conflicts with fishermen. In this study, fisherman–giant otter conflicts were analyzed in the Uacari Sustainable Development Reserve, where giant otters are accused of interfering with fisheries by eating the fish (predation), frightening the fish away (local interference), and damaging fishing equipment (direct interference). Interference by predation was analyzed by evaluating overlap in fish species consumption between humans (measured by subsistence and commercial catches) and giant otters. The giant otter diet was assessed from fecal samples, and the human diet through questionnaires. Local and direct interferences were analyzed through fish samples using gillnets and comparing capture efficiency with and without giant otters’ presence. The overlap between human and giant otter diets was low (0.37), varied seasonally, and was smaller in the low water (0.24) than in the high water period (0.60), when both species tend to be more generalists. Overlap between fish species consumed by giant otters and those exploited by commercial fisheries was small (0.34). Giant otter presence during the experimental fishing was low (9.5%), restricted to the high water period, and did not significantly reduce the captures (<em>U </em>=<em> </em>13, <em>P </em>=<em> </em>0.61). The low overlap in diet may be a result of differences in preferences and fishing strategies. The conflict between giant otters and fishermen is greater in the high water period, when the income of the fisheries decreases; however, the conflict seems to be mainly motivated by the resident's prejudice against giant otters.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>The recovery of giant otter populations after the hunting prohibition and restriction of the pelt trade resulted in more frequent conflicts with fishermen. In this study, fisherman–giant otter conflicts were analyzed in the Uacari Sustainable Development Reserve, where giant otters are accused of interfering with fisheries by eating the fish (predation), frightening the fish away (local interference), and damaging fishing equipment (direct interference). Interference by predation was analyzed by evaluating overlap in fish species consumption between humans (measured by subsistence and commercial catches) and giant otters. The giant otter diet was assessed from fecal samples, and the human diet through questionnaires. Local and direct interferences were analyzed through fish samples using gillnets and comparing capture efficiency with and without giant otters’ presence. The overlap between human and giant otter diets was low (0.37), varied seasonally, and was smaller in the low water (0.24) than in the high water period (0.60), when both species tend to be more generalists. Overlap between fish species consumed by giant otters and those exploited by commercial fisheries was small (0.34). Giant otter presence during the experimental fishing was low (9.5%), restricted to the high water period, and did not significantly reduce the captures (U = 13, P = 0.61). The low overlap in diet may be a result of differences in preferences and fishing strategies. The conflict between giant otters and fishermen is greater in the high water period, when the income of the fisheries decreases; however, the conflict seems to be mainly motivated by the resident's prejudice against giant otters.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00827.x" xmlns="http://purl.org/rss/1.0/"><title>Marine-derived Nutrients from Green Turtle Nests Subsidize Terrestrial Beach Ecosystems</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00827.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Marine-derived Nutrients from Green Turtle Nests Subsidize Terrestrial Beach Ecosystems</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hannah B. Vander Zanden</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Karen A. Bjorndal</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Patrick W. Inglett</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alan B. Bolten</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-14T08:44:08.997202-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00827.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.1744-7429.2011.00827.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00827.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Spatially separated ecosystems are often linked by nutrient fluxes. Nutrient inputs may be transferred by physical vectors (<em>i</em>.<em>e</em>., wind and water) or by biotic vectors. In this study, we examine the role of green turtles (<em>Chelonia mydas</em>) as biotic transporters of nutrients from marine to terrestrial ecosystems, where they deposit eggs. We compare low and high nest density sites at Tortuguero, Costa Rica, the largest green turtle rookery in the western hemisphere. Four plant species (<em>Costus woodsonii</em>, <em>Hibiscus pernanbucensis</em>, <em>Hymenocallis littoralis</em>, <em>Ipomoea pes-caprae</em>) were analyzed at both nest density sites for <sup>15</sup>N, total carbon, nitrogen, and phosphorus, and vegetation cover. Sand was analyzed for <sup>15</sup>N and total nitrogen. Vegetation at high nest density sites had higher total nitrogen, which was correlated with higher δ<sup>15</sup>N values, suggesting nutrient input from a marine source. The dominant plant species changed between low and high nest density sites, indicating that turtle-derived nutrients may alter the plant community composition. The trend in δ<sup>15</sup>N values of sand was similar, although less pronounced than that of the vegetation. Sand may be a poor integrator of nutrient input due to low nutrient adsorption and high rate of leaching. Sea turtles have previously been shown to deposit considerable amounts of nutrients and energy on nesting beaches. In this study, we estimate annual nitrogen and phosphorus contributions at Tortuguero are 507 and 45 kg/km, respectively, and we demonstrate that beach vegetation likely assimilates a portion of these marine-derived nutrients.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Spatially separated ecosystems are often linked by nutrient fluxes. Nutrient inputs may be transferred by physical vectors (i.e., wind and water) or by biotic vectors. In this study, we examine the role of green turtles (Chelonia mydas) as biotic transporters of nutrients from marine to terrestrial ecosystems, where they deposit eggs. We compare low and high nest density sites at Tortuguero, Costa Rica, the largest green turtle rookery in the western hemisphere. Four plant species (Costus woodsonii, Hibiscus pernanbucensis, Hymenocallis littoralis, Ipomoea pes-caprae) were analyzed at both nest density sites for 15N, total carbon, nitrogen, and phosphorus, and vegetation cover. Sand was analyzed for 15N and total nitrogen. Vegetation at high nest density sites had higher total nitrogen, which was correlated with higher δ15N values, suggesting nutrient input from a marine source. The dominant plant species changed between low and high nest density sites, indicating that turtle-derived nutrients may alter the plant community composition. The trend in δ15N values of sand was similar, although less pronounced than that of the vegetation. Sand may be a poor integrator of nutrient input due to low nutrient adsorption and high rate of leaching. Sea turtles have previously been shown to deposit considerable amounts of nutrients and energy on nesting beaches. In this study, we estimate annual nitrogen and phosphorus contributions at Tortuguero are 507 and 45 kg/km, respectively, and we demonstrate that beach vegetation likely assimilates a portion of these marine-derived nutrients.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00834.x" xmlns="http://purl.org/rss/1.0/"><title>Demographic History of Shorea curtisii (Dipterocarpaceae) Inferred from Chloroplast DNA Sequence Variations</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00834.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Demographic History of Shorea curtisii (Dipterocarpaceae) Inferred from Chloroplast DNA Sequence Variations</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Koichi Kamiya</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Satoshi Nanami</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tanaka Kenzo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Reiji Yoneda</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bibian Diway</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lucy Chong</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mohamad A. Azani</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nik M. Majid</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Shawn K. Y. Lum</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Khoon-Meng Wong</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ko Harada</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-14T08:43:59.69603-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00834.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.1744-7429.2011.00834.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00834.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We assessed the variability of chloroplast DNA sequences in populations of the dipterocarp forest tree, <i>Shorea curtisii</i>. This species is widely distributed in hill and coastal hill dipterocarp forests of the Malay Peninsula, whereas isolated populations are found in the coastal hills of north Borneo. Two chloroplast DNA regions (1555 bp of <i>trnH</i><em>-</em><i>psbA</i><em>-</em><i>trnK</i> and 925 bp of <i>trnL</i>-<i>trnF</i>) were sequenced from 123 individuals collected from six Malay Peninsula and two Bornean populations. There were 15 chloroplast haplotypes derived from 16 polymorphic sites. A haplotype network revealed two distinct haplogroups that correlate with two geographic regions, the Malay Peninsula and Borneo. These two haplogroups differed by a number of mutations, and no haplotypes were shared between populations from the different geographic regions. This suggests an ancient diversification of these haplogroups, and that long-distance seed dispersal was unlikely to have occurred during the Pleistocene when the Sunda Shelf was a contiguous landmass. Phylogenetic analysis of the haplotypes together with those found in other <i>Shorea</i> species showed that two haplogroups in <i>S. curtisii</i> appear in different positions of the phylogenetic tree. This could be explained by the persistence of ancestral polymorphisms or by ancient chloroplast capture. Low levels of genetic differentiation were found between populations within each geographic region. Signature of a bottleneck followed by demographic expansion was detected in the Malay Peninsula haplogroup. The presence of two distinct evolutionary lineages in the different regions suggests that they should be managed independently to conserve the major sources of genetic diversity in <i>S. curtisii</i>.</p></div>]]></content:encoded><description>We assessed the variability of chloroplast DNA sequences in populations of the dipterocarp forest tree, Shorea curtisii. This species is widely distributed in hill and coastal hill dipterocarp forests of the Malay Peninsula, whereas isolated populations are found in the coastal hills of north Borneo. Two chloroplast DNA regions (1555 bp of trnH-psbA-trnK and 925 bp of trnL-trnF) were sequenced from 123 individuals collected from six Malay Peninsula and two Bornean populations. There were 15 chloroplast haplotypes derived from 16 polymorphic sites. A haplotype network revealed two distinct haplogroups that correlate with two geographic regions, the Malay Peninsula and Borneo. These two haplogroups differed by a number of mutations, and no haplotypes were shared between populations from the different geographic regions. This suggests an ancient diversification of these haplogroups, and that long-distance seed dispersal was unlikely to have occurred during the Pleistocene when the Sunda Shelf was a contiguous landmass. Phylogenetic analysis of the haplotypes together with those found in other Shorea species showed that two haplogroups in S. curtisii appear in different positions of the phylogenetic tree. This could be explained by the persistence of ancestral polymorphisms or by ancient chloroplast capture. Low levels of genetic differentiation were found between populations within each geographic region. Signature of a bottleneck followed by demographic expansion was detected in the Malay Peninsula haplogroup. The presence of two distinct evolutionary lineages in the different regions suggests that they should be managed independently to conserve the major sources of genetic diversity in S. curtisii.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00821.x" xmlns="http://purl.org/rss/1.0/"><title>Bird Assemblages in Anthropogenic Habitats: Identifying a Suitability Gradient for Native Species in the Atlantic Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00821.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Bird Assemblages in Anthropogenic Habitats: Identifying a Suitability Gradient for Native Species in the Atlantic Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Gustavo A. Zurita</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Maria I. Bellocq</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-12T02:10:48.716298-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00821.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.1744-7429.2011.00821.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00821.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Traditional approaches to the study of species persistence in fragmented landscapes generally consider a binary classification of habitat being suitable or unsuitable; however, the range of human-modified habitats within a region may offer a gradient of habitat suitability (or conservation value) for species. We identified such a gradient by comparing bird assemblages among contrasting land uses (pine plantations of different age, annual crops, clear cuts and cattle pastures) in the Upper Parana Atlantic forest. Bird assemblages and vegetation structure were characterized in an extensive area of 4400 km<sup>2</sup> in Argentina and Paraguay during the breeding seasons of 2005–2010. Similarity of bird assemblages between anthropogenic habitats and the native forest and the proportion of forest species increased with vegetation vertical structure, while the proportion of open-area species decreased. As a consequence, mature tree plantations were the most suitable habitats for forest species and were mainly used by frugivores and bark insectivores. In contrast, open habitats were the least suitable habitat for forest species and were used primarily by insectivores. Human-created habitats that are structurally complex can be used by a subset of forest species, and may improve functional connectivity and mitigate edge effects. The conservation of large tracks of native forests, however, is critical for the long-term persistence of the entire bird assemblage, especially for native forest dependent species.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Traditional approaches to the study of species persistence in fragmented landscapes generally consider a binary classification of habitat being suitable or unsuitable; however, the range of human-modified habitats within a region may offer a gradient of habitat suitability (or conservation value) for species. We identified such a gradient by comparing bird assemblages among contrasting land uses (pine plantations of different age, annual crops, clear cuts and cattle pastures) in the Upper Parana Atlantic forest. Bird assemblages and vegetation structure were characterized in an extensive area of 4400 km2 in Argentina and Paraguay during the breeding seasons of 2005–2010. Similarity of bird assemblages between anthropogenic habitats and the native forest and the proportion of forest species increased with vegetation vertical structure, while the proportion of open-area species decreased. As a consequence, mature tree plantations were the most suitable habitats for forest species and were mainly used by frugivores and bark insectivores. In contrast, open habitats were the least suitable habitat for forest species and were used primarily by insectivores. Human-created habitats that are structurally complex can be used by a subset of forest species, and may improve functional connectivity and mitigate edge effects. The conservation of large tracks of native forests, however, is critical for the long-term persistence of the entire bird assemblage, especially for native forest dependent species.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00822.x" xmlns="http://purl.org/rss/1.0/"><title>Exploitation of Fallen Diaspores by Ants: Are there Ant–Plant Partner Choices?</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00822.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Exploitation of Fallen Diaspores by Ants: Are there Ant–Plant Partner Choices?</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alexander V. Christianini</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Antônio J. Mayhé-Nunes</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paulo S. Oliveira</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-12T02:10:32.462203-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00822.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.1744-7429.2011.00822.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00822.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Ants frequently interact with fleshy fallen diaspores (fruits or seeds) not adapted for ant-dispersal. Such interactions are usually considered as opportunistic, but recent evidence has indicated that these ants may differ in their effects on diaspore survival and plant recruitment. We investigated if partner choices are recognizable among genera of ants and plants, and if ant and plant traits may influence such preferences in cerrado (savanna-like vegetation) from southeast Brazil. During a 2-yr period, 521 ant–diaspore interactions were recorded through various methods, yielding 71 ant species and 38 plant species. Exploitation of fallen diaspores was common among several ant genera, and included carnivorous, omnivorous, and fungivorous ants. Contrary to others areas around the world, where true myrmecochory (seed dispersal by ants) is common among shrubs, ants also exploited diaspores from several cerrado trees. Plant life form, diaspore size, and ant body size did not seem to explain the pattern of interactions observed. Two subsets of preferential interactions, however, segregated fungivorous ants from another group composed of carnivorous and omnivorous ants, probably influenced by the chemical composition of the plant diaspores. Omnivorous ants usually remove the fleshy portion of diaspores on spot and probably provide limited benefits to plants. Carnivorous and fungivorous ants usually remove the whole diaspore to the nest. As each of these ant groups may influence the fitness of diaspores in different ways, there are possible subtle pathways for the evolution of partner choices between ants and these non-myrmecochorous diaspores.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>Ants frequently interact with fleshy fallen diaspores (fruits or seeds) not adapted for ant-dispersal. Such interactions are usually considered as opportunistic, but recent evidence has indicated that these ants may differ in their effects on diaspore survival and plant recruitment. We investigated if partner choices are recognizable among genera of ants and plants, and if ant and plant traits may influence such preferences in cerrado (savanna-like vegetation) from southeast Brazil. During a 2-yr period, 521 ant–diaspore interactions were recorded through various methods, yielding 71 ant species and 38 plant species. Exploitation of fallen diaspores was common among several ant genera, and included carnivorous, omnivorous, and fungivorous ants. Contrary to others areas around the world, where true myrmecochory (seed dispersal by ants) is common among shrubs, ants also exploited diaspores from several cerrado trees. Plant life form, diaspore size, and ant body size did not seem to explain the pattern of interactions observed. Two subsets of preferential interactions, however, segregated fungivorous ants from another group composed of carnivorous and omnivorous ants, probably influenced by the chemical composition of the plant diaspores. Omnivorous ants usually remove the fleshy portion of diaspores on spot and probably provide limited benefits to plants. Carnivorous and fungivorous ants usually remove the whole diaspore to the nest. As each of these ant groups may influence the fitness of diaspores in different ways, there are possible subtle pathways for the evolution of partner choices between ants and these non-myrmecochorous diaspores.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00824.x" xmlns="http://purl.org/rss/1.0/"><title>Spillover of Insects from Rain Forest into Adjacent Oil Palm Plantations</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00824.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Spillover of Insects from Rain Forest into Adjacent Oil Palm Plantations</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jennifer M. Lucey</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jane K. Hill</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-12T02:10:28.455674-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00824.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.1744-7429.2011.00824.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00824.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Conversion of natural forest to oil palm plantations is a major threat to biodiversity in Southeast Asia. The retention of natural forest habitats within plantations has been proposed as a method to reduce biodiversity losses in agricultural areas, and we examined whether forest areas resulted in spillover of species into adjacent oil palm plantations. We sampled ants and butterflies along two 2-km transects across an ecotone from plantation into adjacent forest in Sabah, Malaysian Borneo. Species richness of both taxa was reduced in plantations, but to a greater extent in butterflies (54% reduction) than in ants (25% reduction). Butterfly diversity increased in plantations with increasing proximity to forest primarily due to spillover of ‘vagrant’ forest species (whose larval host plants do not occur in plantations), although richness of species that could potentially breed in plantations also increased near to forest. By contrast, ants showed no spillover effects and were less sensitive to land-use changes, with much higher levels of similarity in species assemblages across habitats than for butterflies. Our results for butterflies suggest that despite the negative impacts of plantations on diversity, proximity to forest could improve diversity in adjacent plantations for some taxa. Spillover of forest species implies that retaining forest areas within plantations may be important for facilitating dispersal of some species through the landscape.</p></div>]]></content:encoded><description>Conversion of natural forest to oil palm plantations is a major threat to biodiversity in Southeast Asia. The retention of natural forest habitats within plantations has been proposed as a method to reduce biodiversity losses in agricultural areas, and we examined whether forest areas resulted in spillover of species into adjacent oil palm plantations. We sampled ants and butterflies along two 2-km transects across an ecotone from plantation into adjacent forest in Sabah, Malaysian Borneo. Species richness of both taxa was reduced in plantations, but to a greater extent in butterflies (54% reduction) than in ants (25% reduction). Butterfly diversity increased in plantations with increasing proximity to forest primarily due to spillover of ‘vagrant’ forest species (whose larval host plants do not occur in plantations), although richness of species that could potentially breed in plantations also increased near to forest. By contrast, ants showed no spillover effects and were less sensitive to land-use changes, with much higher levels of similarity in species assemblages across habitats than for butterflies. Our results for butterflies suggest that despite the negative impacts of plantations on diversity, proximity to forest could improve diversity in adjacent plantations for some taxa. Spillover of forest species implies that retaining forest areas within plantations may be important for facilitating dispersal of some species through the landscape.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00831.x" xmlns="http://purl.org/rss/1.0/"><title>Nitrogen Addition Shapes Soil Phosphorus Availability in Two Reforested Tropical Forests in Southern China</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00831.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Nitrogen Addition Shapes Soil Phosphorus Availability in Two Reforested Tropical Forests in Southern China</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Xiankai Lu</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jiangming Mo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Frank S. Gilliam</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hua Fang</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Feifei Zhu</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Yunting Fang</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Wei Zhang</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Juan Huang</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-12T02:10:23.556577-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00831.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.1744-7429.2011.00831.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00831.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Scant information is available on how soil phosphorus (P) availability responds to atmospheric nitrogen (N) deposition, especially in the tropical zones. This study examined the effect of N addition on soil P availability, and compared this effect between forest sites of contrasting land-use history. Effects of N addition on soil properties, litterfall production, P release from decomposing litter, and soil P availability were studied in a disturbed (reforested pine forest with previous understory vegetation and litter harvesting) and a rehabilitated (reforested mixed pine/broadleaf forest with no understory vegetation and litter harvesting) tropical forest in southern China. Experimental N-treatments (above ambient) were the following: Control (no N addition), N50 (50 kg N ha<sup>−1</sup> yr<sup>−1</sup>), and N100 (100 kg N ha<sup>−1</sup> yr<sup>−1</sup>). Results indicated that N addition significantly decreased soil P availability in the disturbed forest. In the rehabilitated forest, however, soil P availability was significantly increased by N addition. Decreases in soil P availability may be correlated with decreases in rates of P release from decomposing litter in the N-treated plots, whereas the increase in soil P availability was correlated with an increase in litterfall production. Our results suggest that response of soil P availability to N deposition in the reforested tropical forests in southern China may vary greatly with temporal changes in tree species composition and soil nutrient status, caused by different land-use practices.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Chinese is available in the online version of this article.</p></div>]]></content:encoded><description>Scant information is available on how soil phosphorus (P) availability responds to atmospheric nitrogen (N) deposition, especially in the tropical zones. This study examined the effect of N addition on soil P availability, and compared this effect between forest sites of contrasting land-use history. Effects of N addition on soil properties, litterfall production, P release from decomposing litter, and soil P availability were studied in a disturbed (reforested pine forest with previous understory vegetation and litter harvesting) and a rehabilitated (reforested mixed pine/broadleaf forest with no understory vegetation and litter harvesting) tropical forest in southern China. Experimental N-treatments (above ambient) were the following: Control (no N addition), N50 (50 kg N ha−1 yr−1), and N100 (100 kg N ha−1 yr−1). Results indicated that N addition significantly decreased soil P availability in the disturbed forest. In the rehabilitated forest, however, soil P availability was significantly increased by N addition. Decreases in soil P availability may be correlated with decreases in rates of P release from decomposing litter in the N-treated plots, whereas the increase in soil P availability was correlated with an increase in litterfall production. Our results suggest that response of soil P availability to N deposition in the reforested tropical forests in southern China may vary greatly with temporal changes in tree species composition and soil nutrient status, caused by different land-use practices.Abstract in Chinese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00816.x" xmlns="http://purl.org/rss/1.0/"><title>Diets of Frugivorous Bats in Montane Rain Forest and Coffee Plantations in Southeastern Chiapas, Mexico</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00816.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Diets of Frugivorous Bats in Montane Rain Forest and Coffee Plantations in Southeastern Chiapas, Mexico</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carlos García-Estrada</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Anne Damon</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Cornelio Sánchez-Hernández</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lorena Soto-Pinto</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Guillermo Ibarra-Núñez</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-11T11:33:29.62251-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00816.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.1744-7429.2011.00816.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00816.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Frugivorous are one of the main diaspore dispersers in tropical ecosystems, particularly in open areas and sites in the early stages of ecological succession. Frugivorous bat species respond differentially to habitat modification, and in the context of their diaspore dispersal functions it is important to understand species' ecological requirements. We compared the diversity of diaspores, obtained from fecal samples and from fruits carried by frugivorous bats, among five shaded coffee plantations under different management regimes and a montane rain forest in southeastern Chiapas, Mexico. At each site, bats were captured every 2 mo from March 2004 to July 2005, using six mist-nets, during two consecutive nights. We captured 2589 individuals from 18 frugivorous species, from which we collected 969 fecal samples, containing 42 diaspore species associated with early and late successional plants. Although, we captured more frugivorous bat species in montane rain forest, the number of diaspore species in this site (<em>N</em>=14) was not significantly different from the coffee plantations under different management regimes (16–24). In montane rain forest, <em>Sturnira ludovici</em> fed mainly on <em>Piper auritum</em>, but in coffee plantations ate <em>Peperomia</em> sp., <em>Saurauia madrensis, Solanum chrysotrichum</em> and <em>Solanum diphyllum. Artibeus jamaicensis</em> and <em>Artibeus intermedius</em> feed mostly <em>Cecropia obtusifolia</em> and <em>Ficus cookii</em> in all coffee plantations. We suggest that the presence of frugivorous bats in shaded coffee plantations is favored by trees and shrubs associated with secondary and introduced vegetation that farmers have allowed to grow within or around the plantations.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available at <!--TODO: clickthrough URL--><a href="http://onlinelibrary.wiley.com/" title="Link to external resource: http://onlinelibrary.wiley.com/">http://onlinelibrary.wiley.com/</a>.</p></div>]]></content:encoded><description>Frugivorous are one of the main diaspore dispersers in tropical ecosystems, particularly in open areas and sites in the early stages of ecological succession. Frugivorous bat species respond differentially to habitat modification, and in the context of their diaspore dispersal functions it is important to understand species' ecological requirements. We compared the diversity of diaspores, obtained from fecal samples and from fruits carried by frugivorous bats, among five shaded coffee plantations under different management regimes and a montane rain forest in southeastern Chiapas, Mexico. At each site, bats were captured every 2 mo from March 2004 to July 2005, using six mist-nets, during two consecutive nights. We captured 2589 individuals from 18 frugivorous species, from which we collected 969 fecal samples, containing 42 diaspore species associated with early and late successional plants. Although, we captured more frugivorous bat species in montane rain forest, the number of diaspore species in this site (N=14) was not significantly different from the coffee plantations under different management regimes (16–24). In montane rain forest, Sturnira ludovici fed mainly on Piper auritum, but in coffee plantations ate Peperomia sp., Saurauia madrensis, Solanum chrysotrichum and Solanum diphyllum. Artibeus jamaicensis and Artibeus intermedius feed mostly Cecropia obtusifolia and Ficus cookii in all coffee plantations. We suggest that the presence of frugivorous bats in shaded coffee plantations is favored by trees and shrubs associated with secondary and introduced vegetation that farmers have allowed to grow within or around the plantations.Abstract in Spanish is available at http://onlinelibrary.wiley.com/.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00819.x" xmlns="http://purl.org/rss/1.0/"><title>Impact of Hurricane Dean (2007) on Game Species of the Selva Maya, Mexico</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00819.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Impact of Hurricane Dean (2007) on Game Species of the Selva Maya, Mexico</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pablo J. Ramírez-Barajas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Gerald A. Islebe</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sophie Calmé</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-10T00:03:11.97789-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00819.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.1744-7429.2011.00819.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00819.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We assessed the effects of a high-intensity hurricane on the abundance of nine game species in the Yucatan Peninsula, Mexico. We sampled 370 km of linear transects in the 3 yr before the hurricane (<em>i.e</em>., 2003–2005), and 315 km in 3 yr after the hurricane (2008–2010). Relative track abundances of all species declined by two-thirds of their prehurricane values. Abundances of Central American agouti <em>D</em><em>asyprocta punctata</em>, white-tailed deer <em>O</em><em>docoileus virginianus</em>, paca <em>C</em><em>uniculus paca</em>, and Great Curassow <em>C</em><em>rax rubra</em> declined significantly after the hurricane swept the area. Relative track abundances showed a negative, but nonsignificant trend for Ocellated Turkey <em>M</em><em>eleagris ocellata</em>, white-nosed coati <em>N</em><em>asua narica</em>, brocket deer <em>M</em><em>azama</em> sp., and collared peccary <em>P</em><em>ecari tajacu</em>. Only nine-banded armadillo <em>D</em><em>asypus novemcinctus</em> showed a significant increase in abundance. Strictly frugivore and habitat specialist species were more affected than omnivores and habitat generalist species. These latter characteristics, or their combination, seemed advantageous to withstand the stress of habitat disturbance. The trend of posthurricane recovery was incipient for affected species, and it was significant for five species after the impact. Overall, most frugivores and habitat specialists did not reach their prehurricane relative track abundances, and Great Curassow showed no recovery trend. The future expectation of increased frequency and intensity of hurricanes might have severe effects on such species.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Foreign language abstract is available in the online version of this article.</p></div>]]></content:encoded><description>We assessed the effects of a high-intensity hurricane on the abundance of nine game species in the Yucatan Peninsula, Mexico. We sampled 370 km of linear transects in the 3 yr before the hurricane (i.e., 2003–2005), and 315 km in 3 yr after the hurricane (2008–2010). Relative track abundances of all species declined by two-thirds of their prehurricane values. Abundances of Central American agouti Dasyprocta punctata, white-tailed deer Odocoileus virginianus, paca Cuniculus paca, and Great Curassow Crax rubra declined significantly after the hurricane swept the area. Relative track abundances showed a negative, but nonsignificant trend for Ocellated Turkey Meleagris ocellata, white-nosed coati Nasua narica, brocket deer Mazama sp., and collared peccary Pecari tajacu. Only nine-banded armadillo Dasypus novemcinctus showed a significant increase in abundance. Strictly frugivore and habitat specialist species were more affected than omnivores and habitat generalist species. These latter characteristics, or their combination, seemed advantageous to withstand the stress of habitat disturbance. The trend of posthurricane recovery was incipient for affected species, and it was significant for five species after the impact. Overall, most frugivores and habitat specialists did not reach their prehurricane relative track abundances, and Great Curassow showed no recovery trend. The future expectation of increased frequency and intensity of hurricanes might have severe effects on such species.Foreign language abstract is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00820.x" xmlns="http://purl.org/rss/1.0/"><title>Recent Changes in Patch Characteristics and Plant Communities in the Jalca Grasslands of the Peruvian Andes</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00820.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Recent Changes in Patch Characteristics and Plant Communities in the Jalca Grasslands of the Peruvian Andes</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carolina Tovar</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joost F. Duivenvoorden</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Isidoro Sánchez-Vega</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Arie C. Seijmonsbergen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-10T00:03:10.201862-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00820.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.1744-7429.2011.00820.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00820.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Habitat loss and fragmentation are considered major threats to biodiversity, especially in tropical mountain ecosystems. Most studies focus on the relationships between biodiversity and patch characteristics such as patch size, connectivity or degree of contrast with the surrounding matrix, but leave the rate of change within these variables little explored. We analyzed the importance of changes in patch characteristics over time on species diversity and species composition in the paramo of northern Peru, a tropical grassland ecosystem, locally known as jalca. We obtained land use/cover maps for 1987 and 2007 spanning an area of 6300 km<sup>2</sup>, and quantified land use change, jalca patch characteristics and their proportional changes over 20 yr. In 2009, 371 vascular plant species were recorded in 92 plots, each plot representative of single patches. Between 1987 and 2007, jalca cover decreased from 47 to 35 percent due to encroaching agriculture. This activity showed an upward shift probably favored by climate change. The number of jalca patches increased, mean patch size decreased, and the patches showed a higher contrast with the surrounding matrix. Multiple linear regression failed to show that species diversity relates to changes in patch characteristics. Canonical correspondence analysis indicated that species composition relates to the degree of contrast between the patch and its surrounding matrix and its changes through time. We concluded that changes in patch characteristics are important only for species composition. This study highlights the importance of considering matrix management with a long term perspective for conservation efforts.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Habitat loss and fragmentation are considered major threats to biodiversity, especially in tropical mountain ecosystems. Most studies focus on the relationships between biodiversity and patch characteristics such as patch size, connectivity or degree of contrast with the surrounding matrix, but leave the rate of change within these variables little explored. We analyzed the importance of changes in patch characteristics over time on species diversity and species composition in the paramo of northern Peru, a tropical grassland ecosystem, locally known as jalca. We obtained land use/cover maps for 1987 and 2007 spanning an area of 6300 km2, and quantified land use change, jalca patch characteristics and their proportional changes over 20 yr. In 2009, 371 vascular plant species were recorded in 92 plots, each plot representative of single patches. Between 1987 and 2007, jalca cover decreased from 47 to 35 percent due to encroaching agriculture. This activity showed an upward shift probably favored by climate change. The number of jalca patches increased, mean patch size decreased, and the patches showed a higher contrast with the surrounding matrix. Multiple linear regression failed to show that species diversity relates to changes in patch characteristics. Canonical correspondence analysis indicated that species composition relates to the degree of contrast between the patch and its surrounding matrix and its changes through time. We concluded that changes in patch characteristics are important only for species composition. This study highlights the importance of considering matrix management with a long term perspective for conservation efforts.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00799.x" xmlns="http://purl.org/rss/1.0/"><title>The Impact of Cyclone Fanele on a Tropical Dry Forest in Madagascar</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00799.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Impact of Cyclone Fanele on a Tropical Dry Forest in Madagascar</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rebecca J. Lewis</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Katherine H. Bannar-Martin</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-10-27T09:17:27.658757-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00799.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.1744-7429.2011.00799.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00799.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Cyclones, which change tree communities and alter forest structure, are thought to have had a significant selective pressure on the flora and fauna of Madagascar. Very little information, however, is available on the actual impact of cyclones on Malagasy ecosystems. On 21 January 2009, Cyclone Fanele made landfall on the western coast of Madagascar with sustained winds of 185 km/h. We examined the immediate effects of the cyclone on tropical dry forest structure in the Kirindy Mitea National Park. In July and August 2009, we measured the height, diameter at breast height (dbh), and damage for 1361 trees in nine 25 × 25 m plots. We found that: (1) over 95 percent of trees experienced some sort of damage, including 8.8 percent mortality; (2) understory and emergent trees experienced significantly higher mortality than canopy trees; and (3) stem density was reduced 9.2±4.5 percent and biomass was reduced 13.4±8.1 percent after the cyclone. Dbh was the best predictor of trunk damage and mortality. This extensive alteration of forest structure will have a substantial short- and long-term impact on the biotic communities of western Madagascar.</p></div>]]></content:encoded><description>Cyclones, which change tree communities and alter forest structure, are thought to have had a significant selective pressure on the flora and fauna of Madagascar. Very little information, however, is available on the actual impact of cyclones on Malagasy ecosystems. On 21 January 2009, Cyclone Fanele made landfall on the western coast of Madagascar with sustained winds of 185 km/h. We examined the immediate effects of the cyclone on tropical dry forest structure in the Kirindy Mitea National Park. In July and August 2009, we measured the height, diameter at breast height (dbh), and damage for 1361 trees in nine 25 × 25 m plots. We found that: (1) over 95 percent of trees experienced some sort of damage, including 8.8 percent mortality; (2) understory and emergent trees experienced significantly higher mortality than canopy trees; and (3) stem density was reduced 9.2±4.5 percent and biomass was reduced 13.4±8.1 percent after the cyclone. Dbh was the best predictor of trunk damage and mortality. This extensive alteration of forest structure will have a substantial short- and long-term impact on the biotic communities of western Madagascar.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00812.x" xmlns="http://purl.org/rss/1.0/"><title>Evidence for Convergent Evolution in Gape Morphology of the Bat Hawk (Macheiramphus alcinus) with Swifts, Swallows, and Goatsuckers</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00812.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Evidence for Convergent Evolution in Gape Morphology of the Bat Hawk (Macheiramphus alcinus) with Swifts, Swallows, and Goatsuckers</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Landon R. Jones</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hal L. Black</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Clayton M. White</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-10-04T09:27:05.110942-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00812.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.1744-7429.2011.00812.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00812.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Gape morphology has been linked to feeding and breeding ecology in raptors, according to the ingestion rate hypothesis. Mammal feeding raptors have larger gapes, allowing them to ingest prey more rapidly than bird feeders, which have evolved smaller average body sizes and gapes to capture more agile prey. One highly derived raptor, however, the Bat Hawk (<em>Macheiramphus alcinus</em>), specializes on colonial bats and swiftlets concentrated daily in a limited temporal window by capturing and swallowing them whole in flight. We hypothesized that the gape of the Bat Hawk evolved to feed rapidly on agile vertebrates limited temporally. We predicted that the gape of the Bat Hawk would be significantly larger than the gape of other raptors, more closely resembling the gapes of swifts (Apodidae), swallows (Hirundinidae), and goatsuckers (Caprimulgiformes). We measured gape area of the lower mandible in museum specimens representing 138 bird species in six orders. We also compared gape area by prey type in over 100 raptor species in three orders. We predicted that insectivorous raptors would exhibit gapes similar to mammal feeders but would differ from bird feeders because insects are not agile prey. The Bat Hawk had the largest gape of any raptor and more closely resembled the gape of insectivorous birds, which also swallow prey whole in flight. The evolution of an enlarged gape may have permitted the Bat Hawk to exploit a previously unrealized ecological niche. Gapes of bird feeding raptors were smaller than in mammal and insect feeders, supporting the ingestion rate hypothesis.</p></div>]]></content:encoded><description>Gape morphology has been linked to feeding and breeding ecology in raptors, according to the ingestion rate hypothesis. Mammal feeding raptors have larger gapes, allowing them to ingest prey more rapidly than bird feeders, which have evolved smaller average body sizes and gapes to capture more agile prey. One highly derived raptor, however, the Bat Hawk (Macheiramphus alcinus), specializes on colonial bats and swiftlets concentrated daily in a limited temporal window by capturing and swallowing them whole in flight. We hypothesized that the gape of the Bat Hawk evolved to feed rapidly on agile vertebrates limited temporally. We predicted that the gape of the Bat Hawk would be significantly larger than the gape of other raptors, more closely resembling the gapes of swifts (Apodidae), swallows (Hirundinidae), and goatsuckers (Caprimulgiformes). We measured gape area of the lower mandible in museum specimens representing 138 bird species in six orders. We also compared gape area by prey type in over 100 raptor species in three orders. We predicted that insectivorous raptors would exhibit gapes similar to mammal feeders but would differ from bird feeders because insects are not agile prey. The Bat Hawk had the largest gape of any raptor and more closely resembled the gape of insectivorous birds, which also swallow prey whole in flight. The evolution of an enlarged gape may have permitted the Bat Hawk to exploit a previously unrealized ecological niche. Gapes of bird feeding raptors were smaller than in mammal and insect feeders, supporting the ingestion rate hypothesis.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00814.x" xmlns="http://purl.org/rss/1.0/"><title>Avian Habitat Preference in Tropical Forest Restoration in Southern Costa Rica</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00814.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Avian Habitat Preference in Tropical Forest Restoration in Southern Costa Rica</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. Leighton Reid</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. Berton C. Harris</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rakan A. Zahawi</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-26T15:08:10.167412-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00814.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.1744-7429.2011.00814.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00814.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>An important question for tropical forest restoration is whether degraded lands can be actively managed to attract birds. We censused birds and measured vegetation structure at 27 stations in young (6–9-yr old) actively and passively restored pasture and old growth forest at Las Cruces Biological Station in southern Costa Rica. During 481 10-min point counts, we detected a high diversity—186 species—of birds using the restoration area. Surprisingly, species richness and detection frequency did not differ among habitats, and proportional similarity of bird assemblages to old growth forest did not differ between restoration treatments. Bird detection frequency was instead explained by exotic grass cover and understory stem density—vegetation structures that were not strongly impacted by active restoration. The similarity of bird assemblages in actively and passively restored forest may be attributed to differential habitat preferences within and among feeding guilds, low structural contrast between treatments, or the effect of nucleation from actively restored plots into passively restored areas. Rapid recovery of vegetation in this recently restored site is likely due to its proximity to old growth forest and the lack of barriers to effective seed dispersal. Previous restoration studies in highly binary environments (<em>i.e</em>., open pasture vs. tree plantation) have found strong differences in bird abundance and richness. Our data contradict this trend, and suggest that tropical restoration ecologists should carefully consider: (1) when the benefits of active restoration outweigh the cost of implementation; and (2) which avian guilds should be used to measure restoration success given differential responses to habitat structure.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Foreign language abstract is available in the online version of this article.</p></div>]]></content:encoded><description>An important question for tropical forest restoration is whether degraded lands can be actively managed to attract birds. We censused birds and measured vegetation structure at 27 stations in young (6–9-yr old) actively and passively restored pasture and old growth forest at Las Cruces Biological Station in southern Costa Rica. During 481 10-min point counts, we detected a high diversity—186 species—of birds using the restoration area. Surprisingly, species richness and detection frequency did not differ among habitats, and proportional similarity of bird assemblages to old growth forest did not differ between restoration treatments. Bird detection frequency was instead explained by exotic grass cover and understory stem density—vegetation structures that were not strongly impacted by active restoration. The similarity of bird assemblages in actively and passively restored forest may be attributed to differential habitat preferences within and among feeding guilds, low structural contrast between treatments, or the effect of nucleation from actively restored plots into passively restored areas. Rapid recovery of vegetation in this recently restored site is likely due to its proximity to old growth forest and the lack of barriers to effective seed dispersal. Previous restoration studies in highly binary environments (i.e., open pasture vs. tree plantation) have found strong differences in bird abundance and richness. Our data contradict this trend, and suggest that tropical restoration ecologists should carefully consider: (1) when the benefits of active restoration outweigh the cost of implementation; and (2) which avian guilds should be used to measure restoration success given differential responses to habitat structure.Foreign language abstract is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00813.x" xmlns="http://purl.org/rss/1.0/"><title>Soil Effects on Forest Structure and Diversity in a Moist and a Dry Tropical Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00813.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Soil Effects on Forest Structure and Diversity in a Moist and a Dry Tropical Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marielos Peña-Claros</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lourens Poorter</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alfredo Alarcón</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Geoffrey Blate</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Urbano Choque</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Todd S. Fredericksen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marco J. Justiniano</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Claudio Leaño</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Juan Carlos Licona</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">William Pariona</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Francis E. Putz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Lincoln Quevedo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marisol Toledo</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-26T15:07:29.83509-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00813.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.1744-7429.2011.00813.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00813.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Soil characteristics are important drivers of variation in wet tropical forest structure and diversity, but few studies have evaluated these relationships in drier forest types. Using tree and soil data from 48 and 32 1 ha plots, respectively, in a Bolivian moist and dry forest, we asked how soil conditions affect forest structure and diversity within each of the two forest types. After correcting for spatial effects, soil-vegetation relationships differed between the dry and the moist forest, being strongest in the dry forest. Furthermore, we hypothesized that soil nutrients would play a more important role in the moist forest than in the dry forest because vegetation in the moist forest is less constrained by water availability and thus can show its full potential response to soil fertility. However, contrary to our expectations, we found that soil fertility explained a larger number of forest variables in the dry forest (50 percent) than in the moist forest (17 percent). Shannon diversity declined with soil fertility at both sites, probably because the most dominant, shade-tolerant species strongly increased in abundance as soil fertility increased.</p></div>]]></content:encoded><description>Soil characteristics are important drivers of variation in wet tropical forest structure and diversity, but few studies have evaluated these relationships in drier forest types. Using tree and soil data from 48 and 32 1 ha plots, respectively, in a Bolivian moist and dry forest, we asked how soil conditions affect forest structure and diversity within each of the two forest types. After correcting for spatial effects, soil-vegetation relationships differed between the dry and the moist forest, being strongest in the dry forest. Furthermore, we hypothesized that soil nutrients would play a more important role in the moist forest than in the dry forest because vegetation in the moist forest is less constrained by water availability and thus can show its full potential response to soil fertility. However, contrary to our expectations, we found that soil fertility explained a larger number of forest variables in the dry forest (50 percent) than in the moist forest (17 percent). Shannon diversity declined with soil fertility at both sites, probably because the most dominant, shade-tolerant species strongly increased in abundance as soil fertility increased.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00815.x" xmlns="http://purl.org/rss/1.0/"><title>Effects of Climate Change on the Potential Species Richness of Mesoamerican Forests</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00815.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of Climate Change on the Potential Species Richness of Mesoamerican Forests</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Duncan J. Golicher</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luis Cayuela</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Adrian C. Newton</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-26T15:07:23.038555-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00815.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.1744-7429.2011.00815.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00815.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The realized species richness of tropical forests cannot yet be reliably mapped at a regional scale due to lack of systematically collected data. An estimate of the potential species richness (PSR), however, can be produced through the use of species distribution modelling. PSR is interpretable as a climatically determined upper limit to observed species richness. We mapped current PSR and future PSR under climate change scenarios for Mesoamerica by combining the spatial distributions of 2000 tree species as predicted by generalized additive models built from herbaria records and climate layers. An explanatory regression tree was used to extract conditional rules describing the relationship between PSR and climate. The results were summarized by country, ecoregion and protected area status in order to investigate current and possible future variability in PSR in the context of regional biodiversity conservation. Length of the dry season was found to be the key determinant of PSR. Protected areas were found to have higher median PSR values than unprotected areas in most of the countries within the study area. Areas with exceptionally high PSR, however, remain unprotected throughout the region. Neither changes in realized species richness nor extinctions will necessarily follow changes in modelled PSR under climate change. However model output suggests that an increase in temperature of around 3°C, combined with a 20 percent decrease in rainfall could lead to a widespread reduction of around 15 percent of current PSR, with values of up to 40 percent in some moist lower montane tropical forests. The modelled PSR of dry forest ecoregions was found to be relatively stable. Some cooler upper montane forests in northern Mesoamerica, where few species of tropical origin are currently found, may gain PSR if species are free to migrate.</p></div>]]></content:encoded><description>The realized species richness of tropical forests cannot yet be reliably mapped at a regional scale due to lack of systematically collected data. An estimate of the potential species richness (PSR), however, can be produced through the use of species distribution modelling. PSR is interpretable as a climatically determined upper limit to observed species richness. We mapped current PSR and future PSR under climate change scenarios for Mesoamerica by combining the spatial distributions of 2000 tree species as predicted by generalized additive models built from herbaria records and climate layers. An explanatory regression tree was used to extract conditional rules describing the relationship between PSR and climate. The results were summarized by country, ecoregion and protected area status in order to investigate current and possible future variability in PSR in the context of regional biodiversity conservation. Length of the dry season was found to be the key determinant of PSR. Protected areas were found to have higher median PSR values than unprotected areas in most of the countries within the study area. Areas with exceptionally high PSR, however, remain unprotected throughout the region. Neither changes in realized species richness nor extinctions will necessarily follow changes in modelled PSR under climate change. However model output suggests that an increase in temperature of around 3°C, combined with a 20 percent decrease in rainfall could lead to a widespread reduction of around 15 percent of current PSR, with values of up to 40 percent in some moist lower montane tropical forests. The modelled PSR of dry forest ecoregions was found to be relatively stable. Some cooler upper montane forests in northern Mesoamerica, where few species of tropical origin are currently found, may gain PSR if species are free to migrate.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00809.x" xmlns="http://purl.org/rss/1.0/"><title>Moderate Human Disturbance of Rain Forest Alters Composition of Fruiting Plant and Bird Communities</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00809.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Moderate Human Disturbance of Rain Forest Alters Composition of Fruiting Plant and Bird Communities</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kara L. Lefevre</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sapna Sharma</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">F. Helen Rodd</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-26T15:07:19.517432-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00809.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.1744-7429.2011.00809.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00809.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Forests worldwide are experiencing rapid environmental change due to human activity. We aimed to increase understanding of anthropogenic impacts on community composition and species interactions. In a natural experiment, we asked whether subsistence human land use has altered the community composition of a Neotropical rain forest on the island of Tobago, in the West Indies. We surveyed fruiting plants and birds in three adjacent habitat types that varied in level of disturbance, and used multivariate analyses to determine whether changes in the plant community were associated with differences in avifauna composition. The three forest habitats had similar plant and bird diversities, yet markedly different species compositions and abundances. Primary forest had the most diverse plant community, while disturbed habitats had a more homogeneous plant composition. Primary and disturbed forest had distinct community compositions, with canopy cover and the relative abundance of plant types explaining 83 percent of the variation in bird species assemblages. Seemingly moderate human disturbance has led to substantial changes in the plant and bird assemblages of Tobago's rain forest, outside of a protected reserve. Our study highlights the direct links between human disturbance and the structure of rain forests, underscoring the impact of even moderate activity on community composition.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Foreign language abstract is available in the online version of this article.</p></div>]]></content:encoded><description>Forests worldwide are experiencing rapid environmental change due to human activity. We aimed to increase understanding of anthropogenic impacts on community composition and species interactions. In a natural experiment, we asked whether subsistence human land use has altered the community composition of a Neotropical rain forest on the island of Tobago, in the West Indies. We surveyed fruiting plants and birds in three adjacent habitat types that varied in level of disturbance, and used multivariate analyses to determine whether changes in the plant community were associated with differences in avifauna composition. The three forest habitats had similar plant and bird diversities, yet markedly different species compositions and abundances. Primary forest had the most diverse plant community, while disturbed habitats had a more homogeneous plant composition. Primary and disturbed forest had distinct community compositions, with canopy cover and the relative abundance of plant types explaining 83 percent of the variation in bird species assemblages. Seemingly moderate human disturbance has led to substantial changes in the plant and bird assemblages of Tobago's rain forest, outside of a protected reserve. Our study highlights the direct links between human disturbance and the structure of rain forests, underscoring the impact of even moderate activity on community composition.Foreign language abstract is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00803.x" xmlns="http://purl.org/rss/1.0/"><title>Diameter Growth of Juvenile Trees after Gap Formation in a Bolivian Rain Forest: Responses are Strongly Species-specific and Size-dependent</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00803.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Diameter Growth of Juvenile Trees after Gap Formation in a Bolivian Rain Forest: Responses are Strongly Species-specific and Size-dependent</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Claudia C. Soliz-Gamboa</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Anne Sandbrink</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pieter A. Zuidema</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-26T15:05:29.891204-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00803.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.1744-7429.2011.00803.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00803.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We evaluated growth responses to gap formation for juvenile individuals of three canopy rain forest species: <em>Peltogyne cf. heterophylla, Clarisia racemosa</em> and <em>Cedrelinga catenaeformis</em>. Gaps were formed during selective logging operations 7 yr before sampling in a Bolivian rain forest. We collected wood samples for tree-ring analyses at different distances to the stump (&lt;10, 10–40 and &gt;40 m) and from trees with different diameters (5–30 cm diameter at breast height [dbh]). Tree-rings width was measured in at least two radii and converted to average diameter growth. Changes in 7-yr median diameter growth before and after selective logging were analyzed. Diameter growth rates significantly increased by 0.7–0.8 mm/yr after gap formation for <em>P. heterophylla</em> and <em>C. catenaeformis</em>, but not for <em>C. racemosa</em>. We applied a multiple regression analysis to explain variation in growth responses of <em>P. heterophylla</em> and <em>C. catenaeformis</em> by distance to logging gap and tree size. For <em>P. heterophylla</em> we found that growth increase occurring close to logging gaps was strongest for large juvenile trees (20–25 cm dbh) and almost absent in small juveniles. For <em>C. catenaeformis</em>, variation in growth responses was not related to tree size or distance to gaps. Our results show that growth responses to gap formation strongly differ across species and tree sizes. This finding calls for caution in the interpretation of growth releases in tree-ring series, as gap formation does not necessarily invoke growth responses and if such growth responses occur, their strength is species- and size specific.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Foreign language abstract is available in the online version of this article.</p></div>]]></content:encoded><description>We evaluated growth responses to gap formation for juvenile individuals of three canopy rain forest species: Peltogyne cf. heterophylla, Clarisia racemosa and Cedrelinga catenaeformis. Gaps were formed during selective logging operations 7 yr before sampling in a Bolivian rain forest. We collected wood samples for tree-ring analyses at different distances to the stump (&lt;10, 10–40 and &gt;40 m) and from trees with different diameters (5–30 cm diameter at breast height [dbh]). Tree-rings width was measured in at least two radii and converted to average diameter growth. Changes in 7-yr median diameter growth before and after selective logging were analyzed. Diameter growth rates significantly increased by 0.7–0.8 mm/yr after gap formation for P. heterophylla and C. catenaeformis, but not for C. racemosa. We applied a multiple regression analysis to explain variation in growth responses of P. heterophylla and C. catenaeformis by distance to logging gap and tree size. For P. heterophylla we found that growth increase occurring close to logging gaps was strongest for large juvenile trees (20–25 cm dbh) and almost absent in small juveniles. For C. catenaeformis, variation in growth responses was not related to tree size or distance to gaps. Our results show that growth responses to gap formation strongly differ across species and tree sizes. This finding calls for caution in the interpretation of growth releases in tree-ring series, as gap formation does not necessarily invoke growth responses and if such growth responses occur, their strength is species- and size specific.Foreign language abstract is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00796.x" xmlns="http://purl.org/rss/1.0/"><title>Fruit Removal and Natural Seed Dispersal of the Brazil Nut Tree (Bertholletia excelsa) in Central Amazonia, Brazil</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00796.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Fruit Removal and Natural Seed Dispersal of the Brazil Nut Tree (Bertholletia excelsa) in Central Amazonia, Brazil</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joanne M. Tuck Haugaasen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Torbjørn Haugaasen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carlos A. Peres</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rogerio Gribel</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Per Wegge</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-13T11:18:58.204307-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00796.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.1744-7429.2011.00796.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00796.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Experimental approaches to study seed dispersal of the Brazil nut tree have hitherto relied on exposed seeds deposited on the forest floor. Here we use a new method to study the natural dispersal by large rodents such as agoutis; tracking experimentally manipulated and tagged fruits containing individually marked seeds. Fruit manipulation did not deter agoutis from handling fruits. We found that agoutis usually moved intact fruits away from their original location below the parent tree before either hiding them or gnawing through the pericarp to access the seeds inside. Most fruits were moved to distances of 15–30 m from their original position, but some fruits could be taken as far as 60 m. A large number of seeds extracted from manipulated fruits appeared to be eaten immediately. Only 27 out of 1740 experimental seeds were found buried in shallow caches, generally within 5 m of the opened fruit. Fruit removal distance accounted for a disproportionate amount of total seed movement and seeds in the current study were dispersed significantly farther than in a previous experiment using exposed seeds, suggesting that classic dispersal experiments of this character may severely underestimate seed dispersal distances. We therefore conclude that the new method provides a more realistic and accurate approach to investigate natural seed dispersal of Brazil nuts and that the removal of fruits from underneath parent trees before being opened is the key to the significantly increased distances at which seeds are dispersed.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>Experimental approaches to study seed dispersal of the Brazil nut tree have hitherto relied on exposed seeds deposited on the forest floor. Here we use a new method to study the natural dispersal by large rodents such as agoutis; tracking experimentally manipulated and tagged fruits containing individually marked seeds. Fruit manipulation did not deter agoutis from handling fruits. We found that agoutis usually moved intact fruits away from their original location below the parent tree before either hiding them or gnawing through the pericarp to access the seeds inside. Most fruits were moved to distances of 15–30 m from their original position, but some fruits could be taken as far as 60 m. A large number of seeds extracted from manipulated fruits appeared to be eaten immediately. Only 27 out of 1740 experimental seeds were found buried in shallow caches, generally within 5 m of the opened fruit. Fruit removal distance accounted for a disproportionate amount of total seed movement and seeds in the current study were dispersed significantly farther than in a previous experiment using exposed seeds, suggesting that classic dispersal experiments of this character may severely underestimate seed dispersal distances. We therefore conclude that the new method provides a more realistic and accurate approach to investigate natural seed dispersal of Brazil nuts and that the removal of fruits from underneath parent trees before being opened is the key to the significantly increased distances at which seeds are dispersed.Abstract in Portuguese is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00794.x" xmlns="http://purl.org/rss/1.0/"><title>Mistletoes Play Different Roles in a Modular Host–Parasite Network</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00794.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Mistletoes Play Different Roles in a Modular Host–Parasite Network</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Julieta Genini</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marina C. Côrtes</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paulo R. Guimarães Jr</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mauro Galetti</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-09-13T11:18:50.125294-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00794.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.1744-7429.2011.00794.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00794.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Antagonistic interactions between host plants and mistletoes often form complex networks of interacting species. Adequate characterization of network organization requires a combination of qualitative and quantitative data. Therefore, we assessed the distribution of interactions between mistletoes and hosts in the Brazilian Pantanal and characterized the network structure in relation to nestedness and modularity. Interactions were highly asymmetric, with mistletoes presenting low host specificity (<em>i.e</em>., weak dependence) and with hosts being highly susceptible to mistletoe-specific infections. We found a non-nested and modular pattern of interactions, wherein each mistletoe species interacted with a particular set of host species. <em>Psittacanthus</em> spp. infected more species and individuals and also caused a high number of infections per individual, whereas the other mistletoes showed a more specialized pattern of infection. For this reason, <em>Psittacanthus</em> spp. were regarded as module hubs while the other mistletoe species showed a peripheral role. We hypothesize that this pattern is primarily the result of different seed dispersal systems. Although all mistletoe species in our study are bird dispersed, the frugivorous assemblage of <em>Psittacanthus</em> spp. is composed of a larger suite of birds, whereas <em>Phoradendron</em> are mainly dispersed by <em>Euphonia</em> species. The larger assemblage of bird species dispersing <em>Psittacanthus</em> seeds may also increase the number of hosts colonized and, consequently, its dominance in the study area. Nevertheless, other restrictions on the interactions among species, such as the differential capacity of mistletoe infections, defense strategies of hosts and habitat types, can also generate or enhance the observed pattern.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>Antagonistic interactions between host plants and mistletoes often form complex networks of interacting species. Adequate characterization of network organization requires a combination of qualitative and quantitative data. Therefore, we assessed the distribution of interactions between mistletoes and hosts in the Brazilian Pantanal and characterized the network structure in relation to nestedness and modularity. Interactions were highly asymmetric, with mistletoes presenting low host specificity (i.e., weak dependence) and with hosts being highly susceptible to mistletoe-specific infections. We found a non-nested and modular pattern of interactions, wherein each mistletoe species interacted with a particular set of host species. Psittacanthus spp. infected more species and individuals and also caused a high number of infections per individual, whereas the other mistletoes showed a more specialized pattern of infection. For this reason, Psittacanthus spp. were regarded as module hubs while the other mistletoe species showed a peripheral role. We hypothesize that this pattern is primarily the result of different seed dispersal systems. Although all mistletoe species in our study are bird dispersed, the frugivorous assemblage of Psittacanthus spp. is composed of a larger suite of birds, whereas Phoradendron are mainly dispersed by Euphonia species. The larger assemblage of bird species dispersing Psittacanthus seeds may also increase the number of hosts colonized and, consequently, its dominance in the study area. Nevertheless, other restrictions on the interactions among species, such as the differential capacity of mistletoe infections, defense strategies of hosts and habitat types, can also generate or enhance the observed pattern.Abstract in Portuguese is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00795.x" xmlns="http://purl.org/rss/1.0/"><title>Consequences of Fragmentation of Tropical Moist Forest for Birds and Their Role in Predation of Herbivorous Insects</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00795.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Consequences of Fragmentation of Tropical Moist Forest for Birds and Their Role in Predation of Herbivorous Insects</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Betsabé Ruiz-Guerra</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Katherine Renton</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rodolfo Dirzo</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-08-16T08:56:39.341414-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00795.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.1744-7429.2011.00795.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00795.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The consequences of habitat alteration on the role of understory insectivorous birds as predators of herbivorous insects in tropical forests are poorly understood. To examine whether fragmentation may affect the top–down controls of herbivory, we compared the number of species, individuals, and the community structure of insectivorous birds between fragments and continuous tropical moist forest in Mexico. We also registered insect herbivore abundances and conducted a larvae predation experiment to evaluate the potential role of insectivorous birds as predators of herbivorous insects. We recorded 63 bird species from 22 families, 43 percent of which were insectivorous birds. Species richness, abundance, and diversity of the avian community were higher in continuous forest compared with forest fragments. For insectivorous birds in particular, there was low similarity in avian insectivore communities between forest types, and forest fragments had more heavily dominated communities of avian insectivores. During the dry season, forest fragments presented significantly higher predation rates on artificial caterpillars, and lower abundance of herbivorous Lepidoptera larvae, compared with continuous forest. Furthermore, there was a significant negative correlation between artificial caterpillar predation rate and larval Lepidoptera abundance, with higher rates of predation in sample sites of low Lepidoptera abundance. Hence, the potentially greater light in the dry season combined with a more dominated avian insectivore community in forest fragments may facilitate increased predation by avian insectivores, resulting in a decline in abundance of larval Lepidoptera, with implications for the process of insect-driven herbivory in forest fragments.</p></div>]]></content:encoded><description>The consequences of habitat alteration on the role of understory insectivorous birds as predators of herbivorous insects in tropical forests are poorly understood. To examine whether fragmentation may affect the top–down controls of herbivory, we compared the number of species, individuals, and the community structure of insectivorous birds between fragments and continuous tropical moist forest in Mexico. We also registered insect herbivore abundances and conducted a larvae predation experiment to evaluate the potential role of insectivorous birds as predators of herbivorous insects. We recorded 63 bird species from 22 families, 43 percent of which were insectivorous birds. Species richness, abundance, and diversity of the avian community were higher in continuous forest compared with forest fragments. For insectivorous birds in particular, there was low similarity in avian insectivore communities between forest types, and forest fragments had more heavily dominated communities of avian insectivores. During the dry season, forest fragments presented significantly higher predation rates on artificial caterpillars, and lower abundance of herbivorous Lepidoptera larvae, compared with continuous forest. Furthermore, there was a significant negative correlation between artificial caterpillar predation rate and larval Lepidoptera abundance, with higher rates of predation in sample sites of low Lepidoptera abundance. Hence, the potentially greater light in the dry season combined with a more dominated avian insectivore community in forest fragments may facilitate increased predation by avian insectivores, resulting in a decline in abundance of larval Lepidoptera, with implications for the process of insect-driven herbivory in forest fragments.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00801.x" xmlns="http://purl.org/rss/1.0/"><title>Decisions on Temporal Sampling Protocol Influence the Detection of Ecological Patterns</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00801.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Decisions on Temporal Sampling Protocol Influence the Detection of Ecological Patterns</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Cristina Banks-Leite</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert M. Ewers</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rafael G. Pimentel</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jean Paul Metzger</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-08-08T11:45:57.383828-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00801.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.1744-7429.2011.00801.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00801.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Within-site variability in species detectability is a problem common to many biodiversity assessments and can strongly bias the results. Such variability can be caused by many factors, including simple counting inaccuracies, which can be solved by increasing sample size, or by temporal changes in species behavior, meaning that the way the temporal sampling protocol is designed is also very important. Here we use the example of mist-netted tropical birds to determine how design decisions in the temporal sampling protocol can alter the data collected and how these changes might affect the detection of ecological patterns, such as the species-area relationship (SAR). Using data from almost 3400 birds captured from 21,000 net-hours at 31 sites in the Brazilian Atlantic Forest, we found that the magnitude of ecological trends remained fairly stable, but the probability of detecting statistically significant ecological patterns varied depending on sampling effort, time of day and season in which sampling was conducted. For example, more species were detected in the wet season, but the SAR was strongest in the dry season. We found that the temporal distribution of sampling effort was more important than its total amount, discovering that similar ecological results could have been obtained with one-third of the total effort, as long as each site had been equally sampled over 2 yr. We discuss that projects with the same sampling effort and spatial design, but with different temporal sampling protocol are likely to report different ecological patterns, which may ultimately lead to inappropriate conservation strategies.</p></div>]]></content:encoded><description>Within-site variability in species detectability is a problem common to many biodiversity assessments and can strongly bias the results. Such variability can be caused by many factors, including simple counting inaccuracies, which can be solved by increasing sample size, or by temporal changes in species behavior, meaning that the way the temporal sampling protocol is designed is also very important. Here we use the example of mist-netted tropical birds to determine how design decisions in the temporal sampling protocol can alter the data collected and how these changes might affect the detection of ecological patterns, such as the species-area relationship (SAR). Using data from almost 3400 birds captured from 21,000 net-hours at 31 sites in the Brazilian Atlantic Forest, we found that the magnitude of ecological trends remained fairly stable, but the probability of detecting statistically significant ecological patterns varied depending on sampling effort, time of day and season in which sampling was conducted. For example, more species were detected in the wet season, but the SAR was strongest in the dry season. We found that the temporal distribution of sampling effort was more important than its total amount, discovering that similar ecological results could have been obtained with one-third of the total effort, as long as each site had been equally sampled over 2 yr. We discuss that projects with the same sampling effort and spatial design, but with different temporal sampling protocol are likely to report different ecological patterns, which may ultimately lead to inappropriate conservation strategies.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00797.x" xmlns="http://purl.org/rss/1.0/"><title>Contrasting Effects of Fire on Arboreal and Ground-Dwelling Ant Communities of a Neotropical Savanna</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00797.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Contrasting Effects of Fire on Arboreal and Ground-Dwelling Ant Communities of a Neotropical Savanna</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tiago L. M. Frizzo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ricardo I. Campos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Heraldo L. Vasconcelos</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-08-08T11:45:34.224011-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00797.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.1744-7429.2011.00797.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00797.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Ants are a dominant group in tropical savannas and here we examined the responses of the arboreal and ground-dwelling ant fauna to a fire in a Neotropical savanna (cerrado) reserve in Central Brazil. Ants were collected using pitfall traps and baits placed in trees and on the ground beneath each tree. Of the 36 trees marked along two transects, half (from each transect) were burned and half not. The same trees were sampled 1 wk before and again 3 and 12 mo after the fire. Rarefaction curves and ordination analyses using data from all trees from each side of each transect indicated that overall ant species richness and composition did not change after fire. Fire, however, reduced the mean number of ant species per tree, and increased the mean number of species on the ground. Fire increased the average abundance of specialist predators, Camponotini, and opportunistic species, and decreased that of arboreal specialists. Changes in the ground-dwelling fauna were only detected 12 mo after the fire, while those in the arboreal fauna occurred earlier and were no longer apparent 12 mo after the fire. We suggest that these contrasting results represent mainly an indirect response of the ant communities to fire-induced changes in vegetation. Given the temporary and small scale nature of the effects detected and the overall resilience of the ant fauna, our results indicate that a single fire in the cerrado vegetation does not greatly impact the structure of ant communities in the short term.</p></div>]]></content:encoded><description>Ants are a dominant group in tropical savannas and here we examined the responses of the arboreal and ground-dwelling ant fauna to a fire in a Neotropical savanna (cerrado) reserve in Central Brazil. Ants were collected using pitfall traps and baits placed in trees and on the ground beneath each tree. Of the 36 trees marked along two transects, half (from each transect) were burned and half not. The same trees were sampled 1 wk before and again 3 and 12 mo after the fire. Rarefaction curves and ordination analyses using data from all trees from each side of each transect indicated that overall ant species richness and composition did not change after fire. Fire, however, reduced the mean number of ant species per tree, and increased the mean number of species on the ground. Fire increased the average abundance of specialist predators, Camponotini, and opportunistic species, and decreased that of arboreal specialists. Changes in the ground-dwelling fauna were only detected 12 mo after the fire, while those in the arboreal fauna occurred earlier and were no longer apparent 12 mo after the fire. We suggest that these contrasting results represent mainly an indirect response of the ant communities to fire-induced changes in vegetation. Given the temporary and small scale nature of the effects detected and the overall resilience of the ant fauna, our results indicate that a single fire in the cerrado vegetation does not greatly impact the structure of ant communities in the short term.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00791.x" xmlns="http://purl.org/rss/1.0/"><title>Germination of Epiphytic Bromeliads in Forests and Coffee Plantations: Microclimate and Substrate Effects</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00791.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Germination of Epiphytic Bromeliads in Forests and Coffee Plantations: Microclimate and Substrate Effects</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Peter Hietz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manuela Winkler</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Susanne Scheffknecht</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Karl Hülber</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-25T12:42:52.441292-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00791.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.1744-7429.2011.00791.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00791.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This study explores whether differences in germination ability shape habitat distributions among closely related epiphytic species, particularly in the context of the ability to colonize disturbed habitats. We compared the germination of three epiphytic bromeliad species differing in their ability to colonize secondary arboreal vegetation in natural forests, and in old and young coffee plantations. We asked if germination is related to their distribution within the canopy and between habitats, and the extent to which the substrate (branch) or microclimate affects germination success. <em>Tillandsia viridiflora</em>, a species that is largely restricted to closed forests, had highest germination success in natural forests, <em>Tillandsia juncea</em>, a pioneer species, germinated best in young coffee plantations, and <em>Tillandsia heterophylla</em>, an intermediate species, equally in forests and young plantations. Surprisingly germination rates of all three species were lowest in old plantations. Bryophyte cover on branches had a positive effect on germination of <em>T. viridiflora</em> and <em>T. heterophylla</em>, but <em>T. juncea</em> germination rates were largely independent of climate and substrate. These results show that germination can limit the ability of species to colonize disturbed habitats and also contributes to within-canopy distribution.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>This study explores whether differences in germination ability shape habitat distributions among closely related epiphytic species, particularly in the context of the ability to colonize disturbed habitats. We compared the germination of three epiphytic bromeliad species differing in their ability to colonize secondary arboreal vegetation in natural forests, and in old and young coffee plantations. We asked if germination is related to their distribution within the canopy and between habitats, and the extent to which the substrate (branch) or microclimate affects germination success. Tillandsia viridiflora, a species that is largely restricted to closed forests, had highest germination success in natural forests, Tillandsia juncea, a pioneer species, germinated best in young coffee plantations, and Tillandsia heterophylla, an intermediate species, equally in forests and young plantations. Surprisingly germination rates of all three species were lowest in old plantations. Bryophyte cover on branches had a positive effect on germination of T. viridiflora and T. heterophylla, but T. juncea germination rates were largely independent of climate and substrate. These results show that germination can limit the ability of species to colonize disturbed habitats and also contributes to within-canopy distribution.Abstract in Spanish is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00789.x" xmlns="http://purl.org/rss/1.0/"><title>Self-thinning and Tree Competition in Savannas</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00789.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Self-thinning and Tree Competition in Savannas</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">William B. Sea</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Niall P. Hanan</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-25T12:41:39.107047-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00789.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.1744-7429.2011.00789.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00789.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This paper examines the feasibility of applying self-thinning concepts to savannas and how competition with herbaceous vegetation may modify self-thinning patterns among woody plants in these ecosystems. Competition among woody plants has seldom been invoked as a major explanation for the persistence of herbaceous vegetation in mixed tree–grass ecosystems. On the contrary, the primary resource-based explanations for tree–grass coexistence are based on tree–grass competition (niche-separation) that assumes that trees are inferior competitors unless deeper rooting depths provide them exclusive access to water. Alternative nonresource-based hypotheses postulate that trees are the better competitors, but that tree populations are suppressed by mortality related to fire, herbivores, and other disturbances. If self-thinning of woody plants can be detected in savannas, stronger evidence for resource-limitation and competitive interactions among woody plants would suggest that the primary models of savannas need to be adjusted. We present data from savanna sites in South Africa to suggest that self-thinning among woody plants can be detected in low-disturbance situations, while also showing signs that juvenile trees, more so than adults, are suppressed when growing with herbaceous vegetation in these ecosystems. This finding we suggest is evidence for size-asymmetric competition in savannas.</p></div>]]></content:encoded><description>This paper examines the feasibility of applying self-thinning concepts to savannas and how competition with herbaceous vegetation may modify self-thinning patterns among woody plants in these ecosystems. Competition among woody plants has seldom been invoked as a major explanation for the persistence of herbaceous vegetation in mixed tree–grass ecosystems. On the contrary, the primary resource-based explanations for tree–grass coexistence are based on tree–grass competition (niche-separation) that assumes that trees are inferior competitors unless deeper rooting depths provide them exclusive access to water. Alternative nonresource-based hypotheses postulate that trees are the better competitors, but that tree populations are suppressed by mortality related to fire, herbivores, and other disturbances. If self-thinning of woody plants can be detected in savannas, stronger evidence for resource-limitation and competitive interactions among woody plants would suggest that the primary models of savannas need to be adjusted. We present data from savanna sites in South Africa to suggest that self-thinning among woody plants can be detected in low-disturbance situations, while also showing signs that juvenile trees, more so than adults, are suppressed when growing with herbaceous vegetation in these ecosystems. This finding we suggest is evidence for size-asymmetric competition in savannas.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00788.x" xmlns="http://purl.org/rss/1.0/"><title>Density Effects of a Dominant Understory Herb, Isoglossa woodii (Acanthaceae), on Tree Seedlings of a Subtropical Coastal Dune Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00788.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Density Effects of a Dominant Understory Herb, Isoglossa woodii (Acanthaceae), on Tree Seedlings of a Subtropical Coastal Dune Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Zivanai Tsvuura</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Megan E. Griffiths</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael J. Lawes</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-25T12:41:24.621036-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00788.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.1744-7429.2011.00788.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00788.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Suppression of tree seedlings by the understory is an important ecological filter with implications for tree diversity and dynamics. In a greenhouse competition experiment, we used seedlings of four canopy species from coastal dune forest (<em>Diospyros natalensis, Euclea racemosa, Sideroxylon inerme</em> and <em>Apodytes dimidiata</em>) to examine the relative competitive effects of the dominant understory herb <em>Isoglossa woodii</em> on seedling performance. We manipulated <em>I. woodii</em> density, light and nutrient levels and measured growth responses. Total seedling biomass decreased with density of <em>I. woodii</em>. The magnitude of biomass suppression with competitor density was similar among tree species. Consequently there was no discernable hierarchy of competitive ranking among tree species. The relative growth rate of seedlings decreased at higher densities of <em>I. woodii</em> and increased at higher nutrient levels but was unaffected by variation in light conditions. Aboveground biomass decreased at higher densities of <em>I. woodii</em> and at higher light levels but increased at higher nutrient levels. Size asymmetric competition for light and nutrients may be the major driver of aboveground interactions between tree seedling and <em>I. woodii</em>. While tree species showed no hierarchy of competitive ability their seedlings exhibited equivalent responses to competition from an understory dominant, permitting species coexistence and the maintenance of species diversity.</p></div>]]></content:encoded><description>Suppression of tree seedlings by the understory is an important ecological filter with implications for tree diversity and dynamics. In a greenhouse competition experiment, we used seedlings of four canopy species from coastal dune forest (Diospyros natalensis, Euclea racemosa, Sideroxylon inerme and Apodytes dimidiata) to examine the relative competitive effects of the dominant understory herb Isoglossa woodii on seedling performance. We manipulated I. woodii density, light and nutrient levels and measured growth responses. Total seedling biomass decreased with density of I. woodii. The magnitude of biomass suppression with competitor density was similar among tree species. Consequently there was no discernable hierarchy of competitive ranking among tree species. The relative growth rate of seedlings decreased at higher densities of I. woodii and increased at higher nutrient levels but was unaffected by variation in light conditions. Aboveground biomass decreased at higher densities of I. woodii and at higher light levels but increased at higher nutrient levels. Size asymmetric competition for light and nutrients may be the major driver of aboveground interactions between tree seedling and I. woodii. While tree species showed no hierarchy of competitive ability their seedlings exhibited equivalent responses to competition from an understory dominant, permitting species coexistence and the maintenance of species diversity.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00786.x" xmlns="http://purl.org/rss/1.0/"><title>Plant-Inhabiting Ant Utilizes Chemical Cues for Host Discrimination</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00786.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Plant-Inhabiting Ant Utilizes Chemical Cues for Host Discrimination</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tiffany L. Weir</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Scott Newbold</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jorge M. Vivanco</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Megan van Haren</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christopher Fritchman</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Aaron T. Dossey</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stefan Bartram</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Wilhelm Boland</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eric G. Cosio</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Waltraud Kofer</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-12T09:44:19.384631-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00786.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.1744-7429.2011.00786.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00786.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The Neotropical ant <em>Pseudomyrmex triplarinus</em> is involved in an obligate and complex symbiotic association with <em>Triplaris americana</em> trees. The ants inhabit trunk and branch domatia and respond aggressively to foreign invaders. Their degree of host specificity and basis for recognition of host trees has not been studied. We determined that, in contrast to <em>T. americana</em> seedlings, heterospecific seedlings set around the host trees suffered continuous pruning. Ants also removed 80–100 percent of heterospecific leaves attached to the trunk in contrast to only 10–30 percent of conspecific leaves. True species specificity was demonstrated by the selective removal of leaves from <em>Triplaris poeppigiana</em> pinned to host trees. This selectivity was also observed in a matrix-independent bioassay using leaf cuticular extracts on glass microfiber strips. Strips treated with leaf wax extracts from host trees and pinned to the trunk of host trees received only 42 percent of the number of ant visits recorded on solvent-treated controls by the end of the experiment. Strips treated with extracts of a related species, <em>T. poeppigiana</em>, received 64 percent of the number of ant visits compared with solvent-treated controls. These experiments also suggest that <em>P. triplarinus</em> recognizes surface chemicals of their host tree, independent of the texture or architecture of the carrier material; although these factors may still play some role in recognition. This is the first study that we are aware of to investigate the mechanism of host discrimination related to pruning behavior.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>The Neotropical ant Pseudomyrmex triplarinus is involved in an obligate and complex symbiotic association with Triplaris americana trees. The ants inhabit trunk and branch domatia and respond aggressively to foreign invaders. Their degree of host specificity and basis for recognition of host trees has not been studied. We determined that, in contrast to T. americana seedlings, heterospecific seedlings set around the host trees suffered continuous pruning. Ants also removed 80–100 percent of heterospecific leaves attached to the trunk in contrast to only 10–30 percent of conspecific leaves. True species specificity was demonstrated by the selective removal of leaves from Triplaris poeppigiana pinned to host trees. This selectivity was also observed in a matrix-independent bioassay using leaf cuticular extracts on glass microfiber strips. Strips treated with leaf wax extracts from host trees and pinned to the trunk of host trees received only 42 percent of the number of ant visits recorded on solvent-treated controls by the end of the experiment. Strips treated with extracts of a related species, T. poeppigiana, received 64 percent of the number of ant visits compared with solvent-treated controls. These experiments also suggest that P. triplarinus recognizes surface chemicals of their host tree, independent of the texture or architecture of the carrier material; although these factors may still play some role in recognition. This is the first study that we are aware of to investigate the mechanism of host discrimination related to pruning behavior.Abstract in Spanish is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00784.x" xmlns="http://purl.org/rss/1.0/"><title>Asian Tapirs Are No Elephants When It Comes To Seed Dispersal</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00784.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Asian Tapirs Are No Elephants When It Comes To Seed Dispersal</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ahimsa Campos-Arceiz</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carl Traeholt</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Razak Jaffar</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luis Santamaria</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Richard T. Corlett</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-03T09:47:35.497366-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00784.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.1744-7429.2011.00784.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00784.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The elimination of the largest herbivores (elephants and rhinoceroses) from many forests in tropical East Asia may have severe consequences for plant species that depend on them for seed dispersal. We assessed the capacity of Malayan tapirs <em>Tapirus indicus</em>—the next largest nonruminant herbivore in the region—as a substitute for the lost megafauna in this role by studying their ability to disperse the seeds of nine fleshy-fruited plants with seeds 5–97 mm in length. We combined information from feeding trials, germination tests, and field telemetry to assess the effect of tapir consumption on seed viability and to estimate how far the seeds would be dispersed. The tapirs (<em>N</em>=8) ingested few seeds. Seed survival through gut passage was moderately high for small-seeded plants (<em>e.g</em>., 36.9% for <em>Dillenia indica</em>) but very low for medium- (<em>e.g</em>., 7.6% for <em>Tamarindus indica</em>) and large-seeded (<em>e.g</em>., 2.8% for <em>Artocarpus integer</em>) plants. Mean seed gut passage times were long (63–236 h) and only the smallest seeds germinated afterwards. Using movement data from four wild tapirs in Peninsular Malaysia we estimated mean dispersal distances of 917–1287 m (range=22–3289 m) for small-seeded plants. Malayan tapirs effectively dispersed small-seeded plants but acted as seed predators for the large-seeded plants included in our study, suggesting that they cannot replace larger herbivores in seed dispersal. With the absence of elephants and rhinos many megafaunal-syndrome plants in tropical East Asia are expected to face severe dispersal limitation problems.</p></div>]]></content:encoded><description>The elimination of the largest herbivores (elephants and rhinoceroses) from many forests in tropical East Asia may have severe consequences for plant species that depend on them for seed dispersal. We assessed the capacity of Malayan tapirs Tapirus indicus—the next largest nonruminant herbivore in the region—as a substitute for the lost megafauna in this role by studying their ability to disperse the seeds of nine fleshy-fruited plants with seeds 5–97 mm in length. We combined information from feeding trials, germination tests, and field telemetry to assess the effect of tapir consumption on seed viability and to estimate how far the seeds would be dispersed. The tapirs (N=8) ingested few seeds. Seed survival through gut passage was moderately high for small-seeded plants (e.g., 36.9% for Dillenia indica) but very low for medium- (e.g., 7.6% for Tamarindus indica) and large-seeded (e.g., 2.8% for Artocarpus integer) plants. Mean seed gut passage times were long (63–236 h) and only the smallest seeds germinated afterwards. Using movement data from four wild tapirs in Peninsular Malaysia we estimated mean dispersal distances of 917–1287 m (range=22–3289 m) for small-seeded plants. Malayan tapirs effectively dispersed small-seeded plants but acted as seed predators for the large-seeded plants included in our study, suggesting that they cannot replace larger herbivores in seed dispersal. With the absence of elephants and rhinos many megafaunal-syndrome plants in tropical East Asia are expected to face severe dispersal limitation problems.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00785.x" xmlns="http://purl.org/rss/1.0/"><title>Foraging Behavior and Coexistence of Two Sunbird Species in a Kenyan Woodland</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00785.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Foraging Behavior and Coexistence of Two Sunbird Species in a Kenyan Woodland</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joseph O. Oyugi</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joel S. Brown</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christopher J. Whelan</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-02T09:09:15.917024-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00785.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.1744-7429.2011.00785.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00785.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We investigated the mechanism of coexistence of the rare Amani Sunbird (<em>Hedydipna pallidigastra</em>) and the widespread Collared Sunbird (<em>H. collaris</em>), within <em>Brachystegia</em> woodland in the Arabuko-Sokoke Forest, Kenya. We compared how prey abundance and search strategies affect resource exploitation by the two species. We used foraging theory to direct our measures of feeding activities as influenced by sunbird species, tree species and foraging height. We evaluated invertebrate abundance among tree species at different heights within trees. The Collared Sunbird primarily used the understory, and the Amani Sunbird primarily used the upper-canopy. Overall, the rate of prey attacks per flight of the Amani Sunbird was 2.8 times greater than that of the Collared Sunbird. The Amani Sunbird, however, used increased search and attack rates in the understory compared with the mid- and upper-canopies, but the Collared Sunbird foraged similarly throughout all strata. We hypothesize that the increased foraging rate of the Amani in the understory reflects increased foraging costs due to interference from the Collared Sunbird in that stratum. Furthermore, the Collared Sunbird exploits rich patches by moving frequently from place to place. The Amani Sunbird forages slowly, with reduced travel rates, and with a greater number of prey captures within a patch. Arthropod density did not differ among the vegetative strata, but was higher in <em>Brachystegia spiciformis</em> and <em>Hymenaea verrucosa</em> than in six other tree species. We hypothesize that the Amani Sunbird appears dependent upon continued tall <em>B. spiciformis</em> trees within the canopy of the Arabuko-Sokoke Forest.</p></div>]]></content:encoded><description>We investigated the mechanism of coexistence of the rare Amani Sunbird (Hedydipna pallidigastra) and the widespread Collared Sunbird (H. collaris), within Brachystegia woodland in the Arabuko-Sokoke Forest, Kenya. We compared how prey abundance and search strategies affect resource exploitation by the two species. We used foraging theory to direct our measures of feeding activities as influenced by sunbird species, tree species and foraging height. We evaluated invertebrate abundance among tree species at different heights within trees. The Collared Sunbird primarily used the understory, and the Amani Sunbird primarily used the upper-canopy. Overall, the rate of prey attacks per flight of the Amani Sunbird was 2.8 times greater than that of the Collared Sunbird. The Amani Sunbird, however, used increased search and attack rates in the understory compared with the mid- and upper-canopies, but the Collared Sunbird foraged similarly throughout all strata. We hypothesize that the increased foraging rate of the Amani in the understory reflects increased foraging costs due to interference from the Collared Sunbird in that stratum. Furthermore, the Collared Sunbird exploits rich patches by moving frequently from place to place. The Amani Sunbird forages slowly, with reduced travel rates, and with a greater number of prey captures within a patch. Arthropod density did not differ among the vegetative strata, but was higher in Brachystegia spiciformis and Hymenaea verrucosa than in six other tree species. We hypothesize that the Amani Sunbird appears dependent upon continued tall B. spiciformis trees within the canopy of the Arabuko-Sokoke Forest.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00783.x" xmlns="http://purl.org/rss/1.0/"><title>Patterns and Correlates of Tropical Dry Forest Structure and Composition in a Highly Replicated Chronosequence in Yucatan, Mexico</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00783.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Patterns and Correlates of Tropical Dry Forest Structure and Composition in a Highly Replicated Chronosequence in Yucatan, Mexico</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Juan Manuel Dupuy</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">José Luis Hernández-Stefanoni</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rodrigo A. Hernández-Juárez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Erika Tetetla-Rangel</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jorge Omar López-Martínez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eurídice Leyequién-Abarca</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fernando J. Tun-Dzul</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Filogonio May-Pat</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-05-02T09:09:02.491982-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00783.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.1744-7429.2011.00783.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00783.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Research on tropical dry forest (TDF) succession i0s needed for effective conservation and management of this threatened and understudied ecosystem. We used a highly replicated chronosequence within a 37,242-ha TDF landscape to investigate successional patterns by plant size class and to evaluate the influence of stand age, topographic position, soil properties and spatial autocorrelation on forest structure and composition. We used a SPOT5 satellite image to obtain a land-cover thematic map, and sampled woody vegetation (adults: &gt;5 cm diam; saplings: 1–5 cm) and soil properties in 168 plots distributed among four vegetation classes: VC1 (3–8-yr-old forest), VC2 (9–15-yr-old forest), VC3 (&gt;15-yr-old forest on flat areas), VC4 (&gt;15-yr-old forest on hills). Stem density decreased with stand age and was lowest in VC3, while height, basal area and species density increased with age and were higher in older than in younger forests. Topographic position also influenced forest structure and composition. Basal area and height were largely determined by stand age, whereas stem and species density, and composition were influenced mostly by soil variables associated with fertility, and by spatial autocorrelation. Adults and saplings showed contrasting patterns and correlates of community structure, but similar patterns and correlates of composition, possibly due to the prevalence of coppicing. Our results show that our sampling approach can overcome several limitations of chronosequence studies, and provide insights in the patterns and drivers of succession, as well as guidelines for forest management and conservation.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>Research on tropical dry forest (TDF) succession i0s needed for effective conservation and management of this threatened and understudied ecosystem. We used a highly replicated chronosequence within a 37,242-ha TDF landscape to investigate successional patterns by plant size class and to evaluate the influence of stand age, topographic position, soil properties and spatial autocorrelation on forest structure and composition. We used a SPOT5 satellite image to obtain a land-cover thematic map, and sampled woody vegetation (adults: &gt;5 cm diam; saplings: 1–5 cm) and soil properties in 168 plots distributed among four vegetation classes: VC1 (3–8-yr-old forest), VC2 (9–15-yr-old forest), VC3 (&gt;15-yr-old forest on flat areas), VC4 (&gt;15-yr-old forest on hills). Stem density decreased with stand age and was lowest in VC3, while height, basal area and species density increased with age and were higher in older than in younger forests. Topographic position also influenced forest structure and composition. Basal area and height were largely determined by stand age, whereas stem and species density, and composition were influenced mostly by soil variables associated with fertility, and by spatial autocorrelation. Adults and saplings showed contrasting patterns and correlates of community structure, but similar patterns and correlates of composition, possibly due to the prevalence of coppicing. Our results show that our sampling approach can overcome several limitations of chronosequence studies, and provide insights in the patterns and drivers of succession, as well as guidelines for forest management and conservation.Abstract in Spanish is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00781.x" xmlns="http://purl.org/rss/1.0/"><title>Investment in Fine Roots and Arbuscular Mycorrhizal Fungi Decrease During Succession in Three Brazilian Ecosystems</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00781.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Investment in Fine Roots and Arbuscular Mycorrhizal Fungi Decrease During Succession in Three Brazilian Ecosystems</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Waldemar Zangaro</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ricardo A. Alves</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luiz E. Lescano</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Adrielly P. Ansanelo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marco A. Nogueira</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-04-26T08:51:52.326984-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00781.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.1744-7429.2011.00781.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00781.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The functional groups of plants that characterize different phases of succession are expected to show differences in root distribution, fine-root traits and degrees of association with arbuscular mycorrhizal (AM) fungi. The relationship involving fine-root traits and AM fungi that regulate the nutrient acquisition potential among different plant functional groups are still not well understood. We assessed fine-root morphology, AM fungal variables and soil fertility in grassland, secondary forest and mature forest in Atlantic, Araucaria and Pantanal ecosystems in Brazil. Soil cores were collected at 0–10 and 10–20 cm depths. Fine roots were extracted from soil by sieving and root morphological traits and AM colonization were determined. The AM spores were extracted from soil and counted. In all ecosystems, soil fertility, fine-root mass and root diameter increased with the succession, while root length, specific root length, root-hair length, root-hair incidence, AM colonization and AM spore density decreased. These results suggest that plant species from early stages of tropical succession with inherent rapid growth invest in fine roots and maintain a high degree of AM colonization in order to increase the capacity for nutrient acquisition. Conversely, fine root morphological characteristics and low degree of AM colonization exhibited by plants of the later stages of succession lead toward a low nutrient uptake capacity that combine with their typical low growth rates.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>The functional groups of plants that characterize different phases of succession are expected to show differences in root distribution, fine-root traits and degrees of association with arbuscular mycorrhizal (AM) fungi. The relationship involving fine-root traits and AM fungi that regulate the nutrient acquisition potential among different plant functional groups are still not well understood. We assessed fine-root morphology, AM fungal variables and soil fertility in grassland, secondary forest and mature forest in Atlantic, Araucaria and Pantanal ecosystems in Brazil. Soil cores were collected at 0–10 and 10–20 cm depths. Fine roots were extracted from soil by sieving and root morphological traits and AM colonization were determined. The AM spores were extracted from soil and counted. In all ecosystems, soil fertility, fine-root mass and root diameter increased with the succession, while root length, specific root length, root-hair length, root-hair incidence, AM colonization and AM spore density decreased. These results suggest that plant species from early stages of tropical succession with inherent rapid growth invest in fine roots and maintain a high degree of AM colonization in order to increase the capacity for nutrient acquisition. Conversely, fine root morphological characteristics and low degree of AM colonization exhibited by plants of the later stages of succession lead toward a low nutrient uptake capacity that combine with their typical low growth rates.Abstract in Portuguese is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00779.x" xmlns="http://purl.org/rss/1.0/"><title>The Structure of Morphological and Genetic Diversity in Natural Populations of Carica papaya (Caricaceae) in Costa Rica</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00779.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Structure of Morphological and Genetic Diversity in Natural Populations of Carica papaya (Caricaceae) in Costa Rica</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jennifer E. Brown</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jenise M. Bauman</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joseph F. Lawrie</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Oscar J. Rocha</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Richard C. Moore</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-04-26T08:50:26.543921-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00779.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.1744-7429.2011.00779.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00779.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>In Costa Rica, dioecious <em>Carica papaya</em> has been observed growing in disturbed areas and within secondary lowland forests. Such populations can serve as a reservoir of genetic and morphological diversity for this tropical fruit crop. We quantify the levels and patterns of the diversity of naturally occurring populations of <em>C. papaya</em> and address the demographic history of these populations. We measured 29 vegetative and reproductive morphological traits <em>in situ</em> from 252 plants and found significant heterogeneity among regional populations in the majority of these traits. Significant variation was found among regional populations with respect to fruit size and shape, with plants in the Nicoya Peninsula possessing smaller, less fleshy fruit, a characteristic of previously described wild populations of papaya. We then assessed the levels and patterns of genetic diversity in 164 plants from natural populations and 20 cultivars. Natural populations exhibit a deficiency of heterozygotes; however, this is much more pronounced within the cultivars. Although there is little genetic differentiation among natural populations, we did find evidence of cryptic genetic population structure. Analyses of population demography indicate that these natural populations have undergone a recent genetic bottleneck, followed by recent population expansion, possibly promoted by the transformation of the Costa Rican landscape for agricultural use.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>In Costa Rica, dioecious Carica papaya has been observed growing in disturbed areas and within secondary lowland forests. Such populations can serve as a reservoir of genetic and morphological diversity for this tropical fruit crop. We quantify the levels and patterns of the diversity of naturally occurring populations of C. papaya and address the demographic history of these populations. We measured 29 vegetative and reproductive morphological traits in situ from 252 plants and found significant heterogeneity among regional populations in the majority of these traits. Significant variation was found among regional populations with respect to fruit size and shape, with plants in the Nicoya Peninsula possessing smaller, less fleshy fruit, a characteristic of previously described wild populations of papaya. We then assessed the levels and patterns of genetic diversity in 164 plants from natural populations and 20 cultivars. Natural populations exhibit a deficiency of heterozygotes; however, this is much more pronounced within the cultivars. Although there is little genetic differentiation among natural populations, we did find evidence of cryptic genetic population structure. Analyses of population demography indicate that these natural populations have undergone a recent genetic bottleneck, followed by recent population expansion, possibly promoted by the transformation of the Costa Rican landscape for agricultural use.Abstract in Spanish is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00782.x" xmlns="http://purl.org/rss/1.0/"><title>Increased Productivity and Reduced Seed Predation Favor a Large-seeded Palm in Small Atlantic Forest Fragments</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00782.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Increased Productivity and Reduced Seed Predation Favor a Large-seeded Palm in Small Atlantic Forest Fragments</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Cecilia S. Andreazzi</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Clarissa S. Pimenta</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alexandra S. Pires</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fernando A. S. Fernandez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luiz G. Oliveira-Santos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jorge F. S. Menezes</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-04-20T11:20:22.997201-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00782.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.1744-7429.2011.00782.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00782.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Large-seeded plants are especially vulnerable to the loss of seed dispersers in small forest fragments. The palm <em>Attalea humilis</em> goes against this trend by reaching high abundances in small remnants. Productivity, seed dispersal and seed predation of <em>A. humilis</em> were investigated in two large (2400 and 3500 ha) and three small (19, 26 and 57 ha) Atlantic Forest fragments in southeastern Brazil. Palms in the small fragments produced more female inflorescences, resulting in a higher fruit production in these places. Seed dispersal rates were higher in the large fragments, where scatter hoarding was more frequent. Scolytine beetles were the main seed predators and damaged a larger number of seeds in small fragments, but predation by rodents and bruchine beetles was low irrespective of fragment size. As scolytines do not necessarily kill the seeds, low predation by bruchines and rodents, together with its own high productivity, allow <em>A. humilis</em> to be more abundant in small fragments despite the scarcity of its main dispersers. This increased abundance, by its turn, can increase competitive interactions between <em>A. humilis</em> and other plants in small fragments. Thus, abundance patterns of <em>A. humilis</em> are a good example of fragmentation affecting the balance of ecological interactions in a complex way, emphasizing the role of preserving ecological processes for conserving biodiversity in fragmented tropical landscapes.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available at <!--TODO: clickthrough URL--><a href="http://www.blackwell-synergy.com/loi/btp" title="Link to external resource: http://www.blackwell-synergy.com/loi/btp">http://www.blackwell-synergy.com/loi/btp</a>.</p></div>]]></content:encoded><description>Large-seeded plants are especially vulnerable to the loss of seed dispersers in small forest fragments. The palm Attalea humilis goes against this trend by reaching high abundances in small remnants. Productivity, seed dispersal and seed predation of A. humilis were investigated in two large (2400 and 3500 ha) and three small (19, 26 and 57 ha) Atlantic Forest fragments in southeastern Brazil. Palms in the small fragments produced more female inflorescences, resulting in a higher fruit production in these places. Seed dispersal rates were higher in the large fragments, where scatter hoarding was more frequent. Scolytine beetles were the main seed predators and damaged a larger number of seeds in small fragments, but predation by rodents and bruchine beetles was low irrespective of fragment size. As scolytines do not necessarily kill the seeds, low predation by bruchines and rodents, together with its own high productivity, allow A. humilis to be more abundant in small fragments despite the scarcity of its main dispersers. This increased abundance, by its turn, can increase competitive interactions between A. humilis and other plants in small fragments. Thus, abundance patterns of A. humilis are a good example of fragmentation affecting the balance of ecological interactions in a complex way, emphasizing the role of preserving ecological processes for conserving biodiversity in fragmented tropical landscapes.Abstract in Portuguese is available at http://www.blackwell-synergy.com/loi/btp.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00780.x" xmlns="http://purl.org/rss/1.0/"><title>Influence of Grazing on Soil Seed Banks Determines the Restoration Potential of Aboveground Vegetation in a Semi-arid Savanna of Ethiopia</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00780.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Influence of Grazing on Soil Seed Banks Determines the Restoration Potential of Aboveground Vegetation in a Semi-arid Savanna of Ethiopia</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Zewdu K. Tessema</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Willem F. de Boer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert M. T. Baars</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Herbert H. T. Prins</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-04-12T08:16:13.571767-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00780.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.1744-7429.2011.00780.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00780.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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Species composition, number of emerging seedlings, species diversity and functional group of the soil seed banks, and the influence of grazing on the similarity between the soil seed banks and aboveground vegetation, were studied in 2008 and 2009 in a semi-arid savanna of Ethiopia. We tested whether the availability of persistent seeds in the soil could drive the transition from a degraded system under heavy grazing to healthy vegetation with ample perennial grasses. A total of 77 species emerged from the soil seed bank samples: 21 annual grasses, 12 perennial grasses, 4 herbaceous legumes, 39 forbs, and 1 woody species. Perennial grass species dominated the lightly grazed sites, whereas the heavily grazed sites were dominated by annual forbs. Heavy grazing reduced the number of seeds that can germinate in the seed bank. Species richness in the seed bank was, however, not affected by grazing. With increasing soil depth, the seed density and its species richness declined. There was a higher similarity in species composition between the soil seed bank and aboveground vegetation at the lightly grazed sites compared with the heavily grazed sites. The mean similarity between the seed banks and aboveground vegetation was relatively low, indicating the effect of heavy grazing. Moreover, seeds of perennial grasses were less abundant in the soil seed banks under heavy grazing. We concluded that restoration of grass and woody species from the soil seed banks in the heavily grazed areas could not be successful in semi-arid savannas of Ethiopia.</p></div>]]></content:encoded><description>Species composition, number of emerging seedlings, species diversity and functional group of the soil seed banks, and the influence of grazing on the similarity between the soil seed banks and aboveground vegetation, were studied in 2008 and 2009 in a semi-arid savanna of Ethiopia. We tested whether the availability of persistent seeds in the soil could drive the transition from a degraded system under heavy grazing to healthy vegetation with ample perennial grasses. A total of 77 species emerged from the soil seed bank samples: 21 annual grasses, 12 perennial grasses, 4 herbaceous legumes, 39 forbs, and 1 woody species. Perennial grass species dominated the lightly grazed sites, whereas the heavily grazed sites were dominated by annual forbs. Heavy grazing reduced the number of seeds that can germinate in the seed bank. Species richness in the seed bank was, however, not affected by grazing. With increasing soil depth, the seed density and its species richness declined. There was a higher similarity in species composition between the soil seed bank and aboveground vegetation at the lightly grazed sites compared with the heavily grazed sites. The mean similarity between the seed banks and aboveground vegetation was relatively low, indicating the effect of heavy grazing. Moreover, seeds of perennial grasses were less abundant in the soil seed banks under heavy grazing. We concluded that restoration of grass and woody species from the soil seed banks in the heavily grazed areas could not be successful in semi-arid savannas of Ethiopia.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00823.x" xmlns="http://purl.org/rss/1.0/"><title>Removal Effects on Nectar Production in Bat-pollinated Flowers of the Brazilian Cerrado</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00823.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Removal Effects on Nectar Production in Bat-pollinated Flowers of the Brazilian Cerrado</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paulo Estefano D. Bobrowiec</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paulo E. Oliveira</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00823.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.1744-7429.2011.00823.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00823.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Insights</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">5</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We tested the removal effect on nectar production in four bat-pollinated cerrado flowers. We compared the amount of nectar after 7–12 removals with the accumulated nectar in non-manipulated flowers after 12 h. In all, but one species, removals increased volume by 1.5–4.6 times and sugar content by 1.6–4 times, which may affect flower visitation by bats, pollen flow, and reproduction.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>We tested the removal effect on nectar production in four bat-pollinated cerrado flowers. We compared the amount of nectar after 7–12 removals with the accumulated nectar in non-manipulated flowers after 12 h. In all, but one species, removals increased volume by 1.5–4.6 times and sugar content by 1.6–4 times, which may affect flower visitation by bats, pollen flow, and reproduction.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00818.x" xmlns="http://purl.org/rss/1.0/"><title>Lust for Salt in the Western Amazon</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00818.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Lust for Salt in the Western Amazon</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert Dudley</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael Kaspari</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stephen P. Yanoviak</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00818.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.1744-7429.2011.00818.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00818.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Insights</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">6</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">9</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">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Although the use of mineral licks by diverse Amazonian birds and mammals is well-known, the ultimate motivation for such behavior remains unclear. As aerosol deposition of salts declines with distance from oceanic sources, lick visitation in the western Amazon can be explained by demand for sodium, given the low concentration of this micronutrient in the plant tissues consumed by these taxa. Sodium limitation also influences ant foraging behavior, and impinges on ecosystem rates of carbon cycling. The biogeographical context of sodium availability has been largely overlooked, but has substantial pantropical implications for herbivore and decomposer performance in inland rain forests.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Although the use of mineral licks by diverse Amazonian birds and mammals is well-known, the ultimate motivation for such behavior remains unclear. As aerosol deposition of salts declines with distance from oceanic sources, lick visitation in the western Amazon can be explained by demand for sodium, given the low concentration of this micronutrient in the plant tissues consumed by these taxa. Sodium limitation also influences ant foraging behavior, and impinges on ecosystem rates of carbon cycling. The biogeographical context of sodium availability has been largely overlooked, but has substantial pantropical implications for herbivore and decomposer performance in inland rain forests.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00771.x" xmlns="http://purl.org/rss/1.0/"><title>Disturbance Type and Plant Successional Communities in Bahamian Dry Forests</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00771.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Disturbance Type and Plant Successional Communities in Bahamian Dry Forests</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Claire C. Larkin</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Charles Kwit</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joseph M. Wunderle</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eileen H. Helmer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. Henry H. Stevens</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Montara T. K. Roberts</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">David N. Ewert</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00771.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.1744-7429.2011.00771.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00771.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">18</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Different disturbances in similar habitats can produce unique successional assemblages of plants. We collected plant species composition and cover data to investigate the effects of three common types of disturbances—fire, anthropogenic clearing (‘cleared’), and clearing followed by goat grazing (‘cleared-and-grazed’)—on early-successional coppice (dry forest) community structure and development on Eleuthera, Bahamas. For each disturbance type, both the ground layer (&lt;0.5 m height) and shrub layer (&gt;0.5 m height) were sampled in eight patches (&gt;1 ha) of varying age (1–28 yr) since large-scale mature coppice disturbance. Overall, plant communities differed among disturbance types; several common species had significantly higher cover in the shrub layer of fire patches, and cleared-and-grazed patches exhibited higher woody ground cover. Total percent cover in the shrub layer increased in a similar linear fashion along the investigated chronosequence of each disturbance type; however, cover of the common tree species, <em>Bursera simaruba</em>, increased at a notably slower rate in cleared-and-grazed patches. The pattern of increase and subsequent decrease in cover of <em>Lantana</em> spp. and <em>Zanthoxylum fagara</em> in the shrub layer was characterized by longer persistence and higher covers, respectively, in cleared-and-grazed patches, which also exhibited low peak cover and fast decline of nonwoody ground cover. Our results suggest that goats may accelerate some aspects of succession (<em>e.g</em>., quickly removing nonwoody ground cover) and retard other aspects (<em>e.g</em>., inhibiting growth of tree species and maintaining early-successional shrubs in the shrub layer). These effects may lead to different successional trajectories, and have important conservation implications.</p></div>]]></content:encoded><description>Different disturbances in similar habitats can produce unique successional assemblages of plants. We collected plant species composition and cover data to investigate the effects of three common types of disturbances—fire, anthropogenic clearing (‘cleared’), and clearing followed by goat grazing (‘cleared-and-grazed’)—on early-successional coppice (dry forest) community structure and development on Eleuthera, Bahamas. For each disturbance type, both the ground layer (&lt;0.5 m height) and shrub layer (&gt;0.5 m height) were sampled in eight patches (&gt;1 ha) of varying age (1–28 yr) since large-scale mature coppice disturbance. Overall, plant communities differed among disturbance types; several common species had significantly higher cover in the shrub layer of fire patches, and cleared-and-grazed patches exhibited higher woody ground cover. Total percent cover in the shrub layer increased in a similar linear fashion along the investigated chronosequence of each disturbance type; however, cover of the common tree species, Bursera simaruba, increased at a notably slower rate in cleared-and-grazed patches. The pattern of increase and subsequent decrease in cover of Lantana spp. and Zanthoxylum fagara in the shrub layer was characterized by longer persistence and higher covers, respectively, in cleared-and-grazed patches, which also exhibited low peak cover and fast decline of nonwoody ground cover. Our results suggest that goats may accelerate some aspects of succession (e.g., quickly removing nonwoody ground cover) and retard other aspects (e.g., inhibiting growth of tree species and maintaining early-successional shrubs in the shrub layer). These effects may lead to different successional trajectories, and have important conservation implications.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00767.x" xmlns="http://purl.org/rss/1.0/"><title>The Quest for a Suitable Host: Size Distributions of Host Trees and Secondary Hemiepiphytes Search Strategy</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00767.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Quest for a Suitable Host: Size Distributions of Host Trees and Secondary Hemiepiphytes Search Strategy</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">María P. Balcázar-Vargas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">María C. Peñuela-Mora</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tinde R. van Andel</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pieter A. Zuidema</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00767.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.1744-7429.2011.00767.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00767.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">19</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">26</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>As climbing plants lack the capacity to hold themselves upright, they need to encounter a suitable host. Vines, lianas, and secondary hemiepiphytes need, therefore, an effective searching strategy. Various hypotheses have been put forward on searching strategies, including ‘skototropism’—growth toward darkness—and random searching. We studied host searching strategies of three secondary hemiepiphyte species belonging to the genus <em>Heteropsis</em>. We recorded information on the diameter distribution of host and evaluated whether these hosts were ‘suitable’, <em>i.e</em>., sufficiently tall for <em>Heteropsis</em> individuals to reach reproductive size. The diameter distribution of host trees bearing <em>Heteropsis</em> seedlings was similar to that of the trees in our study plots. Also, we found that 72–81 percent of the <em>Heteropsis</em> seedlings were present on unsuitable hosts (seedlings, saplings, herbs). These results suggest that <em>Heteropsis</em> seedlings search hosts in a random manner and not by skototropism. We found quite a distinct pattern for adult <em>Heteropsis</em> individuals, which predominantly occur on host trees bigger than 10 cm dbh. Host diameter distribution for <em>Heteropsis</em> adults differed significantly from that of the entire tree community. This difference suggests that <em>Heteropsis</em> individuals may change hosts if they are initially present on nonsuitable hosts. We observed that <em>Heteropsis</em> seedlings and juveniles on unsuitable hosts often produced vegetative shoots that searched for another host. In many cases, such shoots did not find a suitable host. For <em>Heteropsis</em>, our results suggest that host tree searching is a long-term trial and error process that is governed by a random searching strategy.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>As climbing plants lack the capacity to hold themselves upright, they need to encounter a suitable host. Vines, lianas, and secondary hemiepiphytes need, therefore, an effective searching strategy. Various hypotheses have been put forward on searching strategies, including ‘skototropism’—growth toward darkness—and random searching. We studied host searching strategies of three secondary hemiepiphyte species belonging to the genus Heteropsis. We recorded information on the diameter distribution of host and evaluated whether these hosts were ‘suitable’, i.e., sufficiently tall for Heteropsis individuals to reach reproductive size. The diameter distribution of host trees bearing Heteropsis seedlings was similar to that of the trees in our study plots. Also, we found that 72–81 percent of the Heteropsis seedlings were present on unsuitable hosts (seedlings, saplings, herbs). These results suggest that Heteropsis seedlings search hosts in a random manner and not by skototropism. We found quite a distinct pattern for adult Heteropsis individuals, which predominantly occur on host trees bigger than 10 cm dbh. Host diameter distribution for Heteropsis adults differed significantly from that of the entire tree community. This difference suggests that Heteropsis individuals may change hosts if they are initially present on nonsuitable hosts. We observed that Heteropsis seedlings and juveniles on unsuitable hosts often produced vegetative shoots that searched for another host. In many cases, such shoots did not find a suitable host. For Heteropsis, our results suggest that host tree searching is a long-term trial and error process that is governed by a random searching strategy.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00773.x" xmlns="http://purl.org/rss/1.0/"><title>Fire and Host Abundance as Determinants of the Distribution of Three Congener and Sympatric Mistletoes in an Amazonian Savanna</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00773.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Fire and Host Abundance as Determinants of the Distribution of Three Congener and Sympatric Mistletoes in an Amazonian Savanna</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rodrigo F. Fadini</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Albertina P. Lima</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00773.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.1744-7429.2011.00773.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00773.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">27</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">34</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Most mistletoe species that live in savanna patches are subjected to frequent fires. Although having similar habits, even congener species may parasitize very different host species and show different degrees of specialization that may differentially affect their resistance to fire. We studied three congener mistletoe species with a diverse degree of specificity to their hosts: <em>Psittacanthus biternatus, Psittacanthus eucalyptifolius</em> and <em>Psittacanthus plagiophyllus</em>, the first being the most generalist species, and the last the most specialist. We investigated their prevalence (proportion of hosts infected) in 35 plots of an Amazonian savanna, with different fire histories. Our aim was to understand if they respond similarly to fire frequency and the abundance of their hosts. Additionally, we experimentally applied fire to individuals of the three species using a portable propane flamethrower to test for the influence of mistletoe species, plant size and quantity of heat pulses (single or double burn) on mistletoe survivorship. Prevalence varied greatly among species: 1.5 percent for <em>P. biternatus</em>, 4.8 percent for <em>P. eucalyptifolius</em> and 20 percent for <em>P. plagiophyllus</em>. Prevalence of <em>P. plagiophyllus</em> was negatively related to fire frequency, while for the other two species it was not. <em>Psittacanthus biternatus</em> had a higher probability of survival compared with the other two species, and larger plants were more likely to survive under single burn treatment and to regenerate through sprouting. Our results suggest that, due to complex interactions between fire, hosts and mistletoes, even sympatric species may respond differently to fire frequency and host abundance.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>Most mistletoe species that live in savanna patches are subjected to frequent fires. Although having similar habits, even congener species may parasitize very different host species and show different degrees of specialization that may differentially affect their resistance to fire. We studied three congener mistletoe species with a diverse degree of specificity to their hosts: Psittacanthus biternatus, Psittacanthus eucalyptifolius and Psittacanthus plagiophyllus, the first being the most generalist species, and the last the most specialist. We investigated their prevalence (proportion of hosts infected) in 35 plots of an Amazonian savanna, with different fire histories. Our aim was to understand if they respond similarly to fire frequency and the abundance of their hosts. Additionally, we experimentally applied fire to individuals of the three species using a portable propane flamethrower to test for the influence of mistletoe species, plant size and quantity of heat pulses (single or double burn) on mistletoe survivorship. Prevalence varied greatly among species: 1.5 percent for P. biternatus, 4.8 percent for P. eucalyptifolius and 20 percent for P. plagiophyllus. Prevalence of P. plagiophyllus was negatively related to fire frequency, while for the other two species it was not. Psittacanthus biternatus had a higher probability of survival compared with the other two species, and larger plants were more likely to survive under single burn treatment and to regenerate through sprouting. Our results suggest that, due to complex interactions between fire, hosts and mistletoes, even sympatric species may respond differently to fire frequency and host abundance.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00763.x" xmlns="http://purl.org/rss/1.0/"><title>Tropical Understory Piper Shrubs Maintain High Levels of Genotypic Diversity Despite Frequent Asexual Recruitment</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00763.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Tropical Understory Piper Shrubs Maintain High Levels of Genotypic Diversity Despite Frequent Asexual Recruitment</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eloisa Lasso</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">James W. Dalling</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eldredge Bermingham</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00763.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.1744-7429.2011.00763.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00763.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">35</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">43</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Many plant species have the capacity to regenerate asexually by resprouting from stem and leaf fragments. In the pan-tropical shrub genus <em>Piper</em>, this tendency is thought to be higher in shade-tolerant than light-demanding species, and to represent a trade-off with annual seed production. Here we use molecular markers to identify clones in five <em>Piper</em> species varying in light requirements. We test predictions that (i) asexual recruitment success is highest in shade-tolerant species, and (ii) that consequently, shade-tolerant species are characterized by lower genotypic diversity than light-demanding <em>Piper</em>. We found that two shade-tolerant <em>Piper</em> species recruited asexually more frequently (36–42% of sampled shoots were of asexual origin) than, two light-demanding and one shade-tolerant species (0–26%). Furthermore, as predicted, genotypic diversity was negatively correlated with the frequency of asexual recruitment in the population. Nonetheless, genotypic diversity of <em>Piper</em> was high compared with other clonal plants. The proportion of unique genotypes found per population ranged from 0.58 to 1.0 and the genotypic Simpson's diversity ranged from 0.93 to 1.0 for all five species. Our results suggest that even though asexual reproduction plays an important role in maintaining local populations of <em>Piper</em> in the understory, it does not seem to reduce genotypic diversity to levels that will threaten these species ability to respond to environmental change.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Many plant species have the capacity to regenerate asexually by resprouting from stem and leaf fragments. In the pan-tropical shrub genus Piper, this tendency is thought to be higher in shade-tolerant than light-demanding species, and to represent a trade-off with annual seed production. Here we use molecular markers to identify clones in five Piper species varying in light requirements. We test predictions that (i) asexual recruitment success is highest in shade-tolerant species, and (ii) that consequently, shade-tolerant species are characterized by lower genotypic diversity than light-demanding Piper. We found that two shade-tolerant Piper species recruited asexually more frequently (36–42% of sampled shoots were of asexual origin) than, two light-demanding and one shade-tolerant species (0–26%). Furthermore, as predicted, genotypic diversity was negatively correlated with the frequency of asexual recruitment in the population. Nonetheless, genotypic diversity of Piper was high compared with other clonal plants. The proportion of unique genotypes found per population ranged from 0.58 to 1.0 and the genotypic Simpson's diversity ranged from 0.93 to 1.0 for all five species. Our results suggest that even though asexual reproduction plays an important role in maintaining local populations of Piper in the understory, it does not seem to reduce genotypic diversity to levels that will threaten these species ability to respond to environmental change.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00777.x" xmlns="http://purl.org/rss/1.0/"><title>Subsampling Herbarium Collections to Assess Geographic Diversity Gradients: A Case Study with Endemic Orchidaceae and Rubiaceae in Cameroon</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00777.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Subsampling Herbarium Collections to Assess Geographic Diversity Gradients: A Case Study with Endemic Orchidaceae and Rubiaceae in Cameroon</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Vincent Droissart</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Olivier J. Hardy</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bonaventure Sonké</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Farid Dahdouh-Guebas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tariq Stévart</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00777.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.1744-7429.2011.00777.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00777.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">44</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">52</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We compiled herbarium specimen data to provide an improved characterization of geographic patterns of diversity using indices of species diversity and floristic similarity based on rarefaction principles. A dataset of 3650 georeferenced plant specimens belonging to Orchidaceae and Rubiaceae endemic to Atlantic Central Africa was assembled to assess species composition per half-degree or one-degree grid cells. Local diversity was measured by the expected number of species (<em>S</em><sub><em>k</em></sub>) per grid cell found in subsamples of increasing size and compared with raw species richness (<em>S</em><sub>R</sub>). A nearly unbiased estimator of the effective number of species per grid cell was also used, allowing quantification of ratios of ‘true diversity’ between grid cells. Species turnover was measured using a presence/absence-based similarity index (Sørensen) and an abundance-based index that corrects for sampling bias (<em>NNESS</em>). Our results confirm that the coastal region of Cameroon is more diverse in endemic species than those more inland. The southern part of this coastal forest is, however, as diverse as the more intensively inventoried northern part, and should also be recognized as an important center of endemism. A strong congruence between Sørensen and <em>NNESS</em> similarity matrices lead to similar delimitations of floristic units. Hence, heterogeneous sampling seems to confer more bias when measuring patterns of local diversity using raw species richness than species turnover using Sørensen index. Overall, we argue that subsampling methods represent a useful way to assess diversity gradients using herbarium specimens while correcting for heterogeneous sampling effort.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in French is available in the online version of this article.</p></div>]]></content:encoded><description>We compiled herbarium specimen data to provide an improved characterization of geographic patterns of diversity using indices of species diversity and floristic similarity based on rarefaction principles. A dataset of 3650 georeferenced plant specimens belonging to Orchidaceae and Rubiaceae endemic to Atlantic Central Africa was assembled to assess species composition per half-degree or one-degree grid cells. Local diversity was measured by the expected number of species (Sk) per grid cell found in subsamples of increasing size and compared with raw species richness (SR). A nearly unbiased estimator of the effective number of species per grid cell was also used, allowing quantification of ratios of ‘true diversity’ between grid cells. Species turnover was measured using a presence/absence-based similarity index (Sørensen) and an abundance-based index that corrects for sampling bias (NNESS). Our results confirm that the coastal region of Cameroon is more diverse in endemic species than those more inland. The southern part of this coastal forest is, however, as diverse as the more intensively inventoried northern part, and should also be recognized as an important center of endemism. A strong congruence between Sørensen and NNESS similarity matrices lead to similar delimitations of floristic units. Hence, heterogeneous sampling seems to confer more bias when measuring patterns of local diversity using raw species richness than species turnover using Sørensen index. Overall, we argue that subsampling methods represent a useful way to assess diversity gradients using herbarium specimens while correcting for heterogeneous sampling effort.Abstract in French is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00765.x" xmlns="http://purl.org/rss/1.0/"><title>Insect Herbivory and Leaf Disease in Natural and Human Disturbed Habitats: Lessons from Early-Successional Heliconia Herbs</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00765.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Insect Herbivory and Leaf Disease in Natural and Human Disturbed Habitats: Lessons from Early-Successional Heliconia Herbs</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bráulio A. Santos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Julieta Benítez-Malvido</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00765.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.1744-7429.2011.00765.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00765.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">53</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">62</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The interaction of plants with insect herbivores and fungal pathogens can affect community dynamics, but there is little information on how this antagonistic interaction may be altered in human-disturbed tropical systems. We examined whether the amount and quality of foliar damage on the pioneer herbs <em>Heliconia latispatha</em> and <em>Heliconia collinsiana</em> are distinct on road edges and secondary riparian vegetation compared with natural gaps in continuous forest (controls) in Mexico. We also investigated some physical and biological mechanisms that may jointly explain such differences. The overall insect damage in <em>H. latispatha</em> was similar between road edges and natural forest gaps (8.0% vs. 7.2% of leaf area). Damage by caterpillars, however, decreased from 4.2 percent in forest gaps to 0.5 percent on road edges, whereas damage by leaf-cutting ants increased from 0 to 5.8 percent. In secondary riparian vegetation, where none of the leaves sampled were attacked by ants, overall herbivore damage in <em>H. collinsiana</em> was less than half that observed in forest gaps (3.0% vs. 6.7%), and driven mainly by differences in caterpillar damage (2.5% vs. 6.2%). By contrast, attack by leaf fungal pathogens was two to three times greater in both human-disturbed habitats than in gaps (8.2–9.6% vs. 3.7–4.2%). Potential mechanisms underlying these differences involved human-induced shifts in air and soil temperature driven by greater light availability, as well as changes in relative humidity, leaf toughness, foliar condensed tannins, and local abundance of herbivores. Our results indicate that human disturbance alters insect herbivory and may increase proliferation of leaf disease.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>The interaction of plants with insect herbivores and fungal pathogens can affect community dynamics, but there is little information on how this antagonistic interaction may be altered in human-disturbed tropical systems. We examined whether the amount and quality of foliar damage on the pioneer herbs Heliconia latispatha and Heliconia collinsiana are distinct on road edges and secondary riparian vegetation compared with natural gaps in continuous forest (controls) in Mexico. We also investigated some physical and biological mechanisms that may jointly explain such differences. The overall insect damage in H. latispatha was similar between road edges and natural forest gaps (8.0% vs. 7.2% of leaf area). Damage by caterpillars, however, decreased from 4.2 percent in forest gaps to 0.5 percent on road edges, whereas damage by leaf-cutting ants increased from 0 to 5.8 percent. In secondary riparian vegetation, where none of the leaves sampled were attacked by ants, overall herbivore damage in H. collinsiana was less than half that observed in forest gaps (3.0% vs. 6.7%), and driven mainly by differences in caterpillar damage (2.5% vs. 6.2%). By contrast, attack by leaf fungal pathogens was two to three times greater in both human-disturbed habitats than in gaps (8.2–9.6% vs. 3.7–4.2%). Potential mechanisms underlying these differences involved human-induced shifts in air and soil temperature driven by greater light availability, as well as changes in relative humidity, leaf toughness, foliar condensed tannins, and local abundance of herbivores. Our results indicate that human disturbance alters insect herbivory and may increase proliferation of leaf disease.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00776.x" xmlns="http://purl.org/rss/1.0/"><title>Short-term Effects of Single Species Browsing Release by Different-sized Herbivores on Sand Forest Vegetation Community, South Africa</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00776.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Short-term Effects of Single Species Browsing Release by Different-sized Herbivores on Sand Forest Vegetation Community, South Africa</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Georgette Lagendijk</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bruce R. Page</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rob Slotow</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00776.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.1744-7429.2011.00776.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00776.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">63</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">72</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Manipulations of herbivores in protected areas may have profound effects on ecosystems. We examine short-term effects on tree species assemblages and resource utilization by a mesoherbivore and small-size herbivores (ungulates &lt;20 kg) in Sand Forest, after browsing release from a megaherbivore (elephant), or both a mega- and mesoherbivore (nyala), respectively. Effects were experimentally separated using replicated exclosures where all trees were counted, identified to species and browsing events recorded. Tree species assemblages were impacted by both elephant and nyala, and by each herbivore species individually. Tree turnover rates were higher where both herbivore species were present than in their combined absence. Diet was segregated among elephant, nyala and small-size herbivores. Both resource specificity and browsing pressure by nyala increased in absence of elephant; small-size herbivores increased resource specificity in absence of elephant, and increased browsing pressure in absence of both elephant and nyala. This implies interference competition with competitive release. The indirect effect of the manipulation of herbivore populations, through the removal of one or two herbivore species, caused a shift in tree species composition and diet of smaller-size herbivores. These indirect effects, especially on tree species composition, can become critical as they affect vegetation dynamics, biodiversity and ecosystem processes. Therefore, in order to conserve habitats and biodiversity across all trophic levels, conservation managers should consider the effects of: (1) the full herbivore assemblage present; and (2) any effects of altering the relative and absolute abundance of different herbivore species on other herbivore species and vegetation.</p></div>]]></content:encoded><description>Manipulations of herbivores in protected areas may have profound effects on ecosystems. We examine short-term effects on tree species assemblages and resource utilization by a mesoherbivore and small-size herbivores (ungulates &lt;20 kg) in Sand Forest, after browsing release from a megaherbivore (elephant), or both a mega- and mesoherbivore (nyala), respectively. Effects were experimentally separated using replicated exclosures where all trees were counted, identified to species and browsing events recorded. Tree species assemblages were impacted by both elephant and nyala, and by each herbivore species individually. Tree turnover rates were higher where both herbivore species were present than in their combined absence. Diet was segregated among elephant, nyala and small-size herbivores. Both resource specificity and browsing pressure by nyala increased in absence of elephant; small-size herbivores increased resource specificity in absence of elephant, and increased browsing pressure in absence of both elephant and nyala. This implies interference competition with competitive release. The indirect effect of the manipulation of herbivore populations, through the removal of one or two herbivore species, caused a shift in tree species composition and diet of smaller-size herbivores. These indirect effects, especially on tree species composition, can become critical as they affect vegetation dynamics, biodiversity and ecosystem processes. Therefore, in order to conserve habitats and biodiversity across all trophic levels, conservation managers should consider the effects of: (1) the full herbivore assemblage present; and (2) any effects of altering the relative and absolute abundance of different herbivore species on other herbivore species and vegetation.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00775.x" xmlns="http://purl.org/rss/1.0/"><title>Optimizing Diversity Assessment Protocols for High Canopy Ants in Tropical Rain Forest</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00775.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Optimizing Diversity Assessment Protocols for High Canopy Ants in Tropical Rain Forest</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kalsum M. Yusah</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Tom M. Fayle</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Grant Harris</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">William A. Foster</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00775.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.1744-7429.2011.00775.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00775.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">73</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">81</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The canopies of tropical rain forests support highly diverse, yet poorly known, animal and plant communities. It is vital that researchers who invest the time needed to gain access to the high canopy are able efficiently to survey the animals and plants that they find there. Here, we develop diversity assessment protocols for one of the most ecologically important canopy animal groups, the ants, in lowland dipterocarp rain forest in Sabah, Malaysia. We design and test a novel trap (the purse-string trap) that can be remotely collected, thus avoiding disturbance to ants. We compare this modified trap with two other methods for surveying canopy ants: precision insecticide fogging and baited pitfall trapping. In total, we collected 39,351 ants belonging to 173 species in 38 genera. Fogging collected the most individuals and species, followed by purse-string trapping with baited pitfall trapping catching the fewest. Fogging also resulted in samples with a different species composition to purse-string trapping and baited pitfall trapping, which were not different from one another. Using a ‘greedy algorithm’, which guides the selection of inventory methods in order to maximize new species discovered per researcher-hour, we show that projects allocating fewer than 132 researcher-hours to canopy ant collection and identification should sample exclusively using fogging. Those with more time should use a combination of methods. This prioritization technique could be used to accelerate species discovery in future rapid biodiversity assessments.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Malay is available in the online version of this article.</p></div>]]></content:encoded><description>The canopies of tropical rain forests support highly diverse, yet poorly known, animal and plant communities. It is vital that researchers who invest the time needed to gain access to the high canopy are able efficiently to survey the animals and plants that they find there. Here, we develop diversity assessment protocols for one of the most ecologically important canopy animal groups, the ants, in lowland dipterocarp rain forest in Sabah, Malaysia. We design and test a novel trap (the purse-string trap) that can be remotely collected, thus avoiding disturbance to ants. We compare this modified trap with two other methods for surveying canopy ants: precision insecticide fogging and baited pitfall trapping. In total, we collected 39,351 ants belonging to 173 species in 38 genera. Fogging collected the most individuals and species, followed by purse-string trapping with baited pitfall trapping catching the fewest. Fogging also resulted in samples with a different species composition to purse-string trapping and baited pitfall trapping, which were not different from one another. Using a ‘greedy algorithm’, which guides the selection of inventory methods in order to maximize new species discovered per researcher-hour, we show that projects allocating fewer than 132 researcher-hours to canopy ant collection and identification should sample exclusively using fogging. Those with more time should use a combination of methods. This prioritization technique could be used to accelerate species discovery in future rapid biodiversity assessments.Abstract in Malay is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00768.x" xmlns="http://purl.org/rss/1.0/"><title>Upslope Range Shifts of Andean Dung Beetles in Response to Deforestation: Compounding and Confounding Effects of Microclimatic Change</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00768.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Upslope Range Shifts of Andean Dung Beetles in Response to Deforestation: Compounding and Confounding Effects of Microclimatic Change</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Trond H. Larsen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00768.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.1744-7429.2011.00768.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00768.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">82</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">89</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Warmer, and sometimes drier, conditions associated with global climate change are driving many species to shift poleward and/or upslope. I hypothesized that microclimatic changes related to deforestation cause similar shifts for forest species persisting within degraded landscapes. This appears to be the first study to examine this novel hypothesis. I examined elevational distributions of dung beetle communities along parallel intact and disturbed elevational gradients from 290 to 3450 m asl in the Andes of southeastern Peru. Deforested sites were consistently warmer and drier than forested sites. To maintain the same ambient temperature as in forest, species in a deforested landscape would need to shift on average 489±59 m upslope. Dung beetle species showed a mean upslope range shift of 132±64 m (maximum=743 m) in the deforested landscape. Eight species occurred farther upslope in the degraded landscape, while none shifted downslope. In addition to upper range limit expansions, six species shifting upslope also showed range contractions or population declines at their lower range boundary. High elevation and disturbance-tolerant species did not show range shifts. These findings suggest that land-use change may both confound and compound the influence of global climate change on biodiversity. Synergies between habitat degradation and climate change could more than double previous range shift projections for this century, leading to unexpectedly rapid changes in biodiversity, especially for sensitive organisms such as tropical insects. On the other hand, range shifts caused by habitat degradation may be mistakenly attributed to global climate change.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Warmer, and sometimes drier, conditions associated with global climate change are driving many species to shift poleward and/or upslope. I hypothesized that microclimatic changes related to deforestation cause similar shifts for forest species persisting within degraded landscapes. This appears to be the first study to examine this novel hypothesis. I examined elevational distributions of dung beetle communities along parallel intact and disturbed elevational gradients from 290 to 3450 m asl in the Andes of southeastern Peru. Deforested sites were consistently warmer and drier than forested sites. To maintain the same ambient temperature as in forest, species in a deforested landscape would need to shift on average 489±59 m upslope. Dung beetle species showed a mean upslope range shift of 132±64 m (maximum=743 m) in the deforested landscape. Eight species occurred farther upslope in the degraded landscape, while none shifted downslope. In addition to upper range limit expansions, six species shifting upslope also showed range contractions or population declines at their lower range boundary. High elevation and disturbance-tolerant species did not show range shifts. These findings suggest that land-use change may both confound and compound the influence of global climate change on biodiversity. Synergies between habitat degradation and climate change could more than double previous range shift projections for this century, leading to unexpectedly rapid changes in biodiversity, especially for sensitive organisms such as tropical insects. On the other hand, range shifts caused by habitat degradation may be mistakenly attributed to global climate change.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00774.x" xmlns="http://purl.org/rss/1.0/"><title>The Evolution of Group Stability and Roost Lifespan: Perspectives from Tent-Roosting Bats</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00774.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">The Evolution of Group Stability and Roost Lifespan: Perspectives from Tent-Roosting Bats</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Maria Sagot</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Richard D. Stevens</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00774.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.1744-7429.2011.00774.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00774.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">90</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">97</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Although multiple hypotheses have been proposed to explain group formation, few fully explain the diversity of social interactions found in foliage-roosting bats. Among these bats, tent-roosting species are capable of constructing their own shelters. Although many bats utilize tents previously constructed by other species, it has been suggested that a particular subset of tent-roosting bats specialize on making tents from particular plant species. Tents provide protection from weather and often a place to roost close to foraging sites. Moreover, tent lifespan is plant species specific and may last from a few weeks to more than a year. To better understand effects that roosts have on social bonds of tent-roosting bats, we conducted a literature review to collect information on social systems and tent lifespan. We tested correlated evolution of group stability and group longevity with tent lifespan using Pagel's method for discrete characters. We found that group stability and group longevity are correlated with tent lifespan. That there is correlated evolution between these characters contributes to our understanding of how different mechanisms interact to produce a variety of social systems in mammals.</p></div>]]></content:encoded><description>Although multiple hypotheses have been proposed to explain group formation, few fully explain the diversity of social interactions found in foliage-roosting bats. Among these bats, tent-roosting species are capable of constructing their own shelters. Although many bats utilize tents previously constructed by other species, it has been suggested that a particular subset of tent-roosting bats specialize on making tents from particular plant species. Tents provide protection from weather and often a place to roost close to foraging sites. Moreover, tent lifespan is plant species specific and may last from a few weeks to more than a year. To better understand effects that roosts have on social bonds of tent-roosting bats, we conducted a literature review to collect information on social systems and tent lifespan. We tested correlated evolution of group stability and group longevity with tent lifespan using Pagel's method for discrete characters. We found that group stability and group longevity are correlated with tent lifespan. That there is correlated evolution between these characters contributes to our understanding of how different mechanisms interact to produce a variety of social systems in mammals.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00772.x" xmlns="http://purl.org/rss/1.0/"><title>Monitoring a Puma (Puma concolor) Population in a Fragmented Landscape in Southeast Brazil</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00772.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Monitoring a Puma (Puma concolor) Population in a Fragmented Landscape in Southeast Brazil</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Renata A. Miotto</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marcelo Cervini</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rodrigo A. Begotti</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pedro M. Galetti Jr.</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00772.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.1744-7429.2011.00772.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00772.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">98</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">104</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"><p><b>ABSTRACT</b> The northeast area of São Paulo state has been intensively deforested, resulting in a highly fragmented landscape composed of a few large patches and several small patches of natural vegetation surrounded by sugarcane, eucalyptus, and citrus plantations. In this scenario, we investigated the puma (<em>Puma concolor</em>) population size, sex ratio, and relatedness in two of the last, and largest, natural refuges in the area using a noninvasive method during 2004–2008. By collecting and individualizing fecal samples by microsatellites, we identified 17 individuals, 13 females (76.4%) and 4 males (23.6%) in these areas. Five females were sampled in distinct years and over an extended time and probably represented resident adults. By investigating the relatedness among individual pumas inhabiting the area, we found that only three animals were not related to each other. We also found evidence that young females might establish an adjacent or overlapping territory to their mothers (phylopatry). Moreover, we registered 11 road-killed individuals nearby the study area, ten males and one female, and six human–puma conflicts. The study area may act as a source of individuals that disperse across the matrix to occupy new home ranges, maintaining some degree of gene flow in a source–sink metapopulation structure. Finally, we recommend that puma management should be conducted at the landscape level to provide effective puma conservation in northeastern São Paulo state.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>ABSTRACT The northeast area of São Paulo state has been intensively deforested, resulting in a highly fragmented landscape composed of a few large patches and several small patches of natural vegetation surrounded by sugarcane, eucalyptus, and citrus plantations. In this scenario, we investigated the puma (Puma concolor) population size, sex ratio, and relatedness in two of the last, and largest, natural refuges in the area using a noninvasive method during 2004–2008. By collecting and individualizing fecal samples by microsatellites, we identified 17 individuals, 13 females (76.4%) and 4 males (23.6%) in these areas. Five females were sampled in distinct years and over an extended time and probably represented resident adults. By investigating the relatedness among individual pumas inhabiting the area, we found that only three animals were not related to each other. We also found evidence that young females might establish an adjacent or overlapping territory to their mothers (phylopatry). Moreover, we registered 11 road-killed individuals nearby the study area, ten males and one female, and six human–puma conflicts. The study area may act as a source of individuals that disperse across the matrix to occupy new home ranges, maintaining some degree of gene flow in a source–sink metapopulation structure. Finally, we recommend that puma management should be conducted at the landscape level to provide effective puma conservation in northeastern São Paulo state.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00766.x" xmlns="http://purl.org/rss/1.0/"><title>Differences in Diet Between Spider Monkey Groups Living in Forest Fragments and Continuous Forest in Mexico</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00766.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Differences in Diet Between Spider Monkey Groups Living in Forest Fragments and Continuous Forest in Mexico</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Óscar M. Chaves</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kathryn E. Stoner</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Víctor Arroyo-Rodríguez</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00766.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.1744-7429.2011.00766.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00766.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">105</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">113</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Forest fragmentation can lead to reductions in food availability, especially for some large-bodied tropical mammals such as spider monkeys. During a 15\xE2\x80\x90mo period, we assessed the diet of Geoffroyi's spider monkey (<em>Ateles geoffroyi</em>) in continuous forest and fragments in the Lacandona region, southern Mexico, and related differences in diet to differences in vegetation structure and composition. We found that both forest types presented top food species for monkeys (<em>e.g.</em>, <em>Spondias</em> spp., <em>Brosimum alicastrum</em>), but the sum of the importance value index of these species and the density of large trees were lower in fragments than in continuous forest. We also found that, compared with continuous forest, monkeys in fragments diversified their overall diet, increased consumption of leaves, and reduced the time they spent feeding on trees in favor of more time feeding on hemiepiphytes (particularly <em>Ficus</em> spp.) and palms, both of which were common in fragments. We attribute these changes to the relative food scarcity of the most favored feeding plants in forest fragments. Overall, our findings suggest that monkeys are able to adjust their diet to food availability in fragments, and thus persist in small- and medium-sized fragments. Although it is unlikely that the small size of two of the three study fragments (14 and 31 ha) can maintain viable populations of monkeys in the long term, they may function as stepping stones, facilitating inter-fragment movements and ultimately enhancing seed dispersal in fragmented landscapes.</p></div>]]></content:encoded><description>Forest fragmentation can lead to reductions in food availability, especially for some large-bodied tropical mammals such as spider monkeys. During a 15\xE2\x80\x90mo period, we assessed the diet of Geoffroyi's spider monkey (Ateles geoffroyi) in continuous forest and fragments in the Lacandona region, southern Mexico, and related differences in diet to differences in vegetation structure and composition. We found that both forest types presented top food species for monkeys (e.g., Spondias spp., Brosimum alicastrum), but the sum of the importance value index of these species and the density of large trees were lower in fragments than in continuous forest. We also found that, compared with continuous forest, monkeys in fragments diversified their overall diet, increased consumption of leaves, and reduced the time they spent feeding on trees in favor of more time feeding on hemiepiphytes (particularly Ficus spp.) and palms, both of which were common in fragments. We attribute these changes to the relative food scarcity of the most favored feeding plants in forest fragments. Overall, our findings suggest that monkeys are able to adjust their diet to food availability in fragments, and thus persist in small- and medium-sized fragments. Although it is unlikely that the small size of two of the three study fragments (14 and 31 ha) can maintain viable populations of monkeys in the long term, they may function as stepping stones, facilitating inter-fragment movements and ultimately enhancing seed dispersal in fragmented landscapes.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00769.x" xmlns="http://purl.org/rss/1.0/"><title>Narrow Fungal Mycorrhizal Diversity in a Population of the Orchid Coppensia doniana</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00769.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Narrow Fungal Mycorrhizal Diversity in a Population of the Orchid Coppensia doniana</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rafael B. Valadares</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Marlon C. Pereira</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joel T. Otero</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Elke J. Cardoso</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00769.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.1744-7429.2011.00769.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00769.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">114</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">122</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>In nature, orchids are fully dependent on mycorrhizal fungi to germinate their seeds. These fungi can penetrate root cells and form pelotons, hyphal coils responsible for providing simple sugars for the orchid embryo. During the achlorophyllous seedling stage, orchids depend on fungi; and some species remain dependent through life, while others establish photosynthesis but, to varying degrees, remain facultatively dependent or responsive to fungal colonization as adults. The aim of this study was to identify how many clades of fungi can establish mycorrhizal associations with <em>Coppensia doniana</em>, a widespread orchid in Campos do Jordão (Brazil) and to demonstrate how morphological features can be useful to group and identify these fungi. Plants were collected during the dry season of 2009 near Campos do Jordão State Park. Fungi were isolated by transferring root segments containing pelotons to media. Three main clades of fungi were formed by either qualitative or quantitative morphological data. We identified these fungi as two morphotypes of <em>Ceratorhiza</em> (anamorphic stage of <em>Ceratobasidium</em>) and one uninucleate <em>Rhizoctonia</em>. The internal transcribed spacer (ITS) sequencing data corroborated the morphological features showing the same three clades; all isolates showed a high similarity with <em>Ceratobasidium</em> ITS sequences in GenBank. Thus, it was possible to demonstrate a high affinity between this orchid species of Oncidiinae and <em>Ceratobasidium</em>. Morphological data associated with multivariate statistics proved to be a useful tool in multilevel taxonomy of these orchid-associated fungi.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Portuguese is available in the online version of this article.</p></div>]]></content:encoded><description>In nature, orchids are fully dependent on mycorrhizal fungi to germinate their seeds. These fungi can penetrate root cells and form pelotons, hyphal coils responsible for providing simple sugars for the orchid embryo. During the achlorophyllous seedling stage, orchids depend on fungi; and some species remain dependent through life, while others establish photosynthesis but, to varying degrees, remain facultatively dependent or responsive to fungal colonization as adults. The aim of this study was to identify how many clades of fungi can establish mycorrhizal associations with Coppensia doniana, a widespread orchid in Campos do Jordão (Brazil) and to demonstrate how morphological features can be useful to group and identify these fungi. Plants were collected during the dry season of 2009 near Campos do Jordão State Park. Fungi were isolated by transferring root segments containing pelotons to media. Three main clades of fungi were formed by either qualitative or quantitative morphological data. We identified these fungi as two morphotypes of Ceratorhiza (anamorphic stage of Ceratobasidium) and one uninucleate Rhizoctonia. The internal transcribed spacer (ITS) sequencing data corroborated the morphological features showing the same three clades; all isolates showed a high similarity with Ceratobasidium ITS sequences in GenBank. Thus, it was possible to demonstrate a high affinity between this orchid species of Oncidiinae and Ceratobasidium. Morphological data associated with multivariate statistics proved to be a useful tool in multilevel taxonomy of these orchid-associated fungi.Abstract in Portuguese is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00770.x" xmlns="http://purl.org/rss/1.0/"><title>Patterns and Trends of Forest Loss in the Colombian Guyana</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00770.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Patterns and Trends of Forest Loss in the Colombian Guyana</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nelly Rodríguez</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dolors Armenteras</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Roberto Molowny-Horas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Javier Retana</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00770.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.1744-7429.2011.00770.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00770.x</prism:url><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">123</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">132</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">ABSTRACT</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Spatial patterns of tropical deforestation and fragmentation are conditional upon human settlement characteristics. We analyze four different human occupation models (indigenous, colonist frontier, transition and established settlement) in the Colombian Guyana Shield at three different times: 1985, 1992 and 2002, and compared them for: (1) deforestation rates; (2) the amount of forest as classified according to a fragmentation pattern (interior forest, edge forest, perforated forest and forest patch); (3) various fragmentation metrics using repeated measures analysis of variance; and (4) potential future deforestation trends though the implementation of a spatially explicit simulation model. The indigenous and colonist frontier occupation models had low rates of deforestation (0.04%/yr), while the well-established settlement occupation model had the highest rate (3.68%/yr). Our results indicate that the four occupation models generate three deforestation patterns: diffuse, which can be subdivided into two subpatterns (indigenous and colonist), geometric (transition) and patchy (established settlement). The area with the established settlement model was highly fragmented, while in the transition occupation area, forest loss was gradual and linked to economic activities associated with the expansion of the agricultural frontier. The simulation of future trends revealed that indigenous and colonist areas had a constant, albeit small, loss of forest covers. The other models had a deforestation probability of 0.8 or more. Overall, our results highlight the need for new and urgent policies for reducing forest conversion that consider intraregional variability in human occupation linked to differences in land-use patterns.</p></div><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Abstract in Spanish is available in the online version of this article.</p></div>]]></content:encoded><description>Spatial patterns of tropical deforestation and fragmentation are conditional upon human settlement characteristics. We analyze four different human occupation models (indigenous, colonist frontier, transition and established settlement) in the Colombian Guyana Shield at three different times: 1985, 1992 and 2002, and compared them for: (1) deforestation rates; (2) the amount of forest as classified according to a fragmentation pattern (interior forest, edge forest, perforated forest and forest patch); (3) various fragmentation metrics using repeated measures analysis of variance; and (4) potential future deforestation trends though the implementation of a spatially explicit simulation model. The indigenous and colonist frontier occupation models had low rates of deforestation (0.04%/yr), while the well-established settlement occupation model had the highest rate (3.68%/yr). Our results indicate that the four occupation models generate three deforestation patterns: diffuse, which can be subdivided into two subpatterns (indigenous and colonist), geometric (transition) and patchy (established settlement). The area with the established settlement model was highly fragmented, while in the transition occupation area, forest loss was gradual and linked to economic activities associated with the expansion of the agricultural frontier. The simulation of future trends revealed that indigenous and colonist areas had a constant, albeit small, loss of forest covers. The other models had a deforestation probability of 0.8 or more. Overall, our results highlight the need for new and urgent policies for reducing forest conversion that consider intraregional variability in human occupation linked to differences in land-use patterns.Abstract in Spanish is available in the online version of this article.</description></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00848.x" xmlns="http://purl.org/rss/1.0/"><title>Remembering Prof. Dr. Elisabeth Klara Victoria Kalko (1962–2011)</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00848.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Remembering Prof. Dr. Elisabeth Klara Victoria Kalko (1962–2011)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">K. Eduard Linsenmair</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00848.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.1744-7429.2011.00848.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00848.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Obituary</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">133</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">134</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00849.x" xmlns="http://purl.org/rss/1.0/"><title>Thanks to Editors and ad hoc Reviewers 2010–2011</title><link>http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00849.x</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Thanks to Editors and ad hoc Reviewers 2010–2011</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/j.1744-7429.2011.00849.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.1744-7429.2011.00849.x</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1111%2Fj.1744-7429.2011.00849.x</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Online Materials</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">135</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">138</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item></rdf:RDF>
