Abstract:We investigate the composition of anuran communities of land-bridge islands off the southeastern coast of Brazil. These islands provide natural long-term experiments on the effects of fragmentation in the Brazilian Atlantic Forest (BAF). We hypothesize that Pleistocene sea-level changes, in combination with other abiotic variables such as area and habitat diversity, has affected anuran species richness and community composition on these islands. Data from the literature and collections databases were used to p… Show more
“…NESTEDNESS AND COMMUNITY STRUCTURE.-We did not detect a nested pattern in the anuran communities studied, which contrasts with the nested structure found in other frog communities in islands (Yiming et al 1998, Hecnar et al 2002, Bittencourt-Silva & Silva 2014, ponds (Hecnar & M'Closkey 1997, Werner et al 2007, or forest fragments (Vallan 2000, Watling et al 2009). For example, in a study evaluating the tadpole communities in 37 ponds, those that were found in ponds with high canopy cover, small area, and short hydroperiod were nested subsets of those with contrasting characteristics (Werner et al 2007).…”
Section: Discussioncontrasting
confidence: 81%
“…, Hecnar et al . , Bittencourt‐Silva & Silva ), ponds (Hecnar & M'Closkey , Werner et al . ), or forest fragments (Vallan , Watling et al .…”
Section: Discussionmentioning
confidence: 99%
“…). In frog communities of land‐bridge islands also in the Rio de Janeiro state most lowland ephemeral‐pond breeding frogs were absent, but were abundant in the adjacent mainland (Bittencourt‐Silva & Silva ). A process of selective extinction was suggested as the main driver of nested pattern in these insular frog communities, possibly because of the rise of sea level (Bittencourt‐Silva & Silva ).…”
Section: Discussionmentioning
confidence: 99%
“…Nestedness commonly occurs in animal and plant communities when the sets of species in species-poor sites are subsets of the species present in the species-rich areas (Almeida-Neto et al 2008, Frick et al 2009, Ulrich et al 2009, Wang et al 2010. Selective extinction and colonization may produce nested distribution patterns in patchy environments (Hecnar & M'Closkey 1997, Werner et al 2007, Watling et al 2009, Bittencourt-Silva & Silva 2014, based on the assumptions of island biogeography theory that extinction rates are inversely related to patch area, and that colonization rates are inversely related to patch isolation (MacArthur & Wilson 1967). A nested structure can result from constraints of natural or human origin, such as elevation and habitat heterogeneity, landscape changes, and resource specialization (Ulrich et al 2009, Tinker et al 2012, Torn es & Ruh ı 2013, Dauby et al 2014.…”
The sets of species in animal and plant communities often comprise nested subsets of the species in broader communities. Although most mechanisms causing nested patterns are known and have been demonstrated for different environments and taxa, how amphibian communities are structured in ephemeral ponds in tropical disturbed landscapes remains unknown. We investigated if pond size, duration, presence of trees (local factors), and the proportion of forest cover surrounding ponds (landscape factor) affect anuran species richness and composition, and if pond assemblages showed a nested pattern. We sampled 11 ephemeral ponds in a pasture matrix near a large Atlantic Forest remnant in Brazil and measured local and landscape variables inside two buffer zones around each pond (100 and 500 m). We marked 1514 individuals from 23 anuran species, and found that richness in ponds ranged from 3–14 species. Both local and landscape factors explained frog species richness in the sampled ponds, and seemed to affect community composition. Frog communities occurred in a non‐nested pattern, contrary to our expectations: species found in poor subsets were not found in larger, more complex ponds. Local and landscape characteristics create a variety of environments in ephemeral ponds, even in impoverished ones; these characteristics restrict pond occupancy for some species, and result in a non‐nested pattern.
“…NESTEDNESS AND COMMUNITY STRUCTURE.-We did not detect a nested pattern in the anuran communities studied, which contrasts with the nested structure found in other frog communities in islands (Yiming et al 1998, Hecnar et al 2002, Bittencourt-Silva & Silva 2014, ponds (Hecnar & M'Closkey 1997, Werner et al 2007, or forest fragments (Vallan 2000, Watling et al 2009). For example, in a study evaluating the tadpole communities in 37 ponds, those that were found in ponds with high canopy cover, small area, and short hydroperiod were nested subsets of those with contrasting characteristics (Werner et al 2007).…”
Section: Discussioncontrasting
confidence: 81%
“…, Hecnar et al . , Bittencourt‐Silva & Silva ), ponds (Hecnar & M'Closkey , Werner et al . ), or forest fragments (Vallan , Watling et al .…”
Section: Discussionmentioning
confidence: 99%
“…). In frog communities of land‐bridge islands also in the Rio de Janeiro state most lowland ephemeral‐pond breeding frogs were absent, but were abundant in the adjacent mainland (Bittencourt‐Silva & Silva ). A process of selective extinction was suggested as the main driver of nested pattern in these insular frog communities, possibly because of the rise of sea level (Bittencourt‐Silva & Silva ).…”
Section: Discussionmentioning
confidence: 99%
“…Nestedness commonly occurs in animal and plant communities when the sets of species in species-poor sites are subsets of the species present in the species-rich areas (Almeida-Neto et al 2008, Frick et al 2009, Ulrich et al 2009, Wang et al 2010. Selective extinction and colonization may produce nested distribution patterns in patchy environments (Hecnar & M'Closkey 1997, Werner et al 2007, Watling et al 2009, Bittencourt-Silva & Silva 2014, based on the assumptions of island biogeography theory that extinction rates are inversely related to patch area, and that colonization rates are inversely related to patch isolation (MacArthur & Wilson 1967). A nested structure can result from constraints of natural or human origin, such as elevation and habitat heterogeneity, landscape changes, and resource specialization (Ulrich et al 2009, Tinker et al 2012, Torn es & Ruh ı 2013, Dauby et al 2014.…”
The sets of species in animal and plant communities often comprise nested subsets of the species in broader communities. Although most mechanisms causing nested patterns are known and have been demonstrated for different environments and taxa, how amphibian communities are structured in ephemeral ponds in tropical disturbed landscapes remains unknown. We investigated if pond size, duration, presence of trees (local factors), and the proportion of forest cover surrounding ponds (landscape factor) affect anuran species richness and composition, and if pond assemblages showed a nested pattern. We sampled 11 ephemeral ponds in a pasture matrix near a large Atlantic Forest remnant in Brazil and measured local and landscape variables inside two buffer zones around each pond (100 and 500 m). We marked 1514 individuals from 23 anuran species, and found that richness in ponds ranged from 3–14 species. Both local and landscape factors explained frog species richness in the sampled ponds, and seemed to affect community composition. Frog communities occurred in a non‐nested pattern, contrary to our expectations: species found in poor subsets were not found in larger, more complex ponds. Local and landscape characteristics create a variety of environments in ephemeral ponds, even in impoverished ones; these characteristics restrict pond occupancy for some species, and result in a non‐nested pattern.
“…In the western Caribbean, two species inhabit islands, Micrurus nigrocintus in the Greater Corn Islands and Corn Islands, east of Nicaragua and M. ruatans is the islands of Roatán, off the coast of Honduras (Crother, ), both these islands were connected to the mainland during the Pleistocene (Petuch, ; Woodburne, ). In South America, M. corallinus inhabits several coastal Brazilian islets (Cicchi, Sena, Peccinini‐Seale, & Duarte, ), which were connected to the mainland when sea level fell between 10–20 Kya (Bittencourt‐Silva & Silva, ; Bueno, Schmidt Dias, & Stelle, ; Violante & Parker, ). Hence, New World coral snakes seem to lack the long‐distance dispersal capabilities of other snakes (e.g.…”
In this study, we analyse New World coral snakes in a phylogenetic framework based upon an increased molecular data set, including novel sequences for the only two sympatric species known from an island (Trinidad, West Indies). Their presence in Trinidad and absence in Tobago offers a unique system to study the phylogeography of the region. We assess the tempo and mode of colonisation of Micrurus on the island, in addition to discussing the phylogenetic relationships for the genus Micrurus concerning two phenotypic traits, body and tail banding patterns. These relationships are analysed for the first time on statistical coalescent phylogeographic discrete ancestral reconstruction. We find a robust phylogenetic component in these characteristics, where strongly supported clades are recovered: prior to the onset of the Early Miocene, a triadal and tricolour tail clade composed of species from South America, and a second clade dating to the Middle‐Late‐ Miocene with monadal and bicolour tails widely distributed from North to South America. The divergence between clades dates to the Oligocene and suggests an ancient pre‐isthmus divergence supporting the arrival of the triadal clade into South America, before the connection between Central and South America was established. We find the two coral snakes present in the West Indies, M. diutius and M. circinalis, belong to the triadal and monadal clades, respectively. Guyana and Trinidad Micrurus diutius share the same haplotypes suggesting a Late Pleistocene–Holocene vicariance when sea level rises separated Trinidad from the mainland. A second lineage of diutius‐like snakes is present in Guyana and is confirmed as M. lemniscatus which is assigned as a voucher and restricts the type locality for M. lemniscatus.
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