542 resultados para Amphibians.
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Data of amphibians, reptiles and birds surveyed from February 2016 to May 2016 in the UNESCO Sheka forest biosphere reserve are provided as an online open access data file.
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O conhecimento de como os mamíferos carnívoros de médio e grande porte Neotropicais capturam e manipulam suas presas é incipiente, e algumas espécies podem somente ser investigadas por análises das fezes, e certos presupostos teóricos sobre forrageo podem ser aplicados e testados a partir da análise da dieta. Lontra longicaudis é um mamífero aquático cuja as fezes podem ser facilmente reconhecidas e coletadas para fornecer informação básica referentes a ecologia de forrageamento da espécie. Com base nessa situação, foram desenvolvidas duas questões relacionadas a dieta, como: (I) Se a 30 composição de presas na dieta varia entre as estações ao longo do ano? E qual o tamanho da magnitude do efeito deste fator? (II) Se a amplitude da dieta varia entre as estações? Nós respondemos estas questões por meio da análise das fezes. Foram realizadas 12 expedições mensais para as coletas, em um trecho de 13 quilômetros do baixo curso do Arroio Grande. Cada fezes foi coletada individualmente, e dados como data e posição geografica anotados. As presas foram classificadas por categorias alimentares (peixes, mamíferos, aves, anfíbios, serpentes, crustaceos e insetos) e em nível de família. A alimentação de L. longicaudis foi a baseada em peixes, com uma amplitude de dieta estreita. As famílias Cichlidae e Callichthyidae predominaram na dieta ao longo do ano. A composição de peixes na dieta variou sazonalmente, porém, a amplitude da dieta não variou. Assim Lontra longicaudis caça presas e mantém certo grau de felxibilidade alimentar ao longo do ano.
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A lontra-neotropical (Lontra longicaudis) é um carnívoro semi-aquático, com adaptações morfológicas para viver nos mais diversos habitats aquáticos, como rios, lagos, mangues e estuários. Além disso, também é encontrada em ambientes marinhos, onde se alimenta, ou apenas transita. São carnívoros que se alimentam principalmente de peixes e crustáceos. O objetivo desde trabalho foi verificar a utilização de ambientes de influência do mar, por L. longicaudis, no litoral sul do RS. A área de estudo foi a Praia do Cassino, onde foram percorridos seis cursos d’água (sangradouros), por cerca de 1 km em cada, à procura de fezes de lontras, entre dezembro de 2009 e novembro de 2010. As fezes foram analisadas para determinar a distribuição espaço-temporal e a dieta das lontras. Foram encontradas 75 fezes de lontras, sendo a maior quantidade no inverno e outono, diminuindo na primavera e verão. As maiores quantidades de fezes foram encontradas nos sangradouros R7 e R9, por estes serem mais extensos e profundos. As menores quantidades de fezes nos sangradouros R4, R8 e R10 se deve ao fato de estes serem menores e menos profundos. Os peixes foram as principais presas das lontras, seguidos pelos crustáceos, anfíbios, moluscos, insetos, aves e mamíferos. Os peixes foram mais predados na maior parte das estações, exceto no outono, quando os crustáceos predominaram. No inverno, os anfíbios predominaram sobre os crustáceos, sendo o segundo grupo mais predado. Os peixes mais consumidos foram Perciformes e Siluriformes. Foi verificado que as lontras utilizam os sangradouros da Praia do Cassino, mesmo estes não possuindo vegetação e substrato mais favoráveis à espécie. A maior utilização dos ambientes durante o inverno provavelmente se deve ao fato de neste período os sangradouros estarem mais profundos. A dieta das lontras variou ao longo do ano, possivelmente conforme a disponibilidade das presas.
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Although the value of primary forests for biodiversity conservation is well known, the potential biodiversity and conservation value of regenerating forests remains controversial. Many factors likely contribute to this, including: 1. the variable ages of regenerating forests being studied (often dominated by relatively young regenerating forests); 2. the potential for confounding on-going human disturbance (such as logging and hunting); 3. the relatively low number of multi-taxa studies; 4. the lack of studies that directly compare different historic disturbances within the same location; 5. contrasting patterns from different survey methodologies and the paucity of knowledge on the impacts across different vertical levels of rainforest biodiversity (often due to a lack of suitable methodologies available to assess them). We also know relatively little as to how biodiversity is affected by major current impacts, such as unmarked rainforest roads, which contribute to this degradation of habitat and fragmentation. This thesis explores the potential biodiversity value of regenerating rainforests under the best of scenarios and seeks to understand more about the impact of current human disturbance to biodiversity; data comes from case studies from the Manu and Sumaco Biosphere Reserves in the Western Amazon. Specifically, I compare overall biodiversity and conservation value of a best case regenerating rainforest site with a selection of well-studied primary forest sites and with predicted species lists for the region; including a focus on species of key conservation concern. I then investigate the biodiversity of the same study site in reference to different types of historic anthropogenic disturbance. Following this I investigate the impacts to biodiversity from an unmarked rainforest road. In order to understand more about the differential effects of habitat disturbance on arboreal diversity I directly assess how patterns of butterfly biodiversity vary between three vertical strata. Although assessments within the canopy have been made for birds, invertebrates and bats, very few studies have successfully targeted arboreal mammals. I therefore investigate the potential of camera traps for inventorying arboreal mammal species in comparison with traditional methodologies. Finally, in order to investigate the possibility that different survey methodologies might identify different biodiversity patterns in habitat disturbance assessments, I investigate whether two different but commonly used survey methodologies used to assess amphibians, indicate the same or different responses of amphibian biodiversity to historic habitat change by people. The regenerating rainforest study site contained high levels of species richness; both in terms of alpha diversity found in nearby primary forest areas (87% ±3.5) and in terms of predicted primary forest diversity from the region (83% ±6.7). This included 89% (39 out of 44) of the species of high conservation concern predicted for the Manu region. Faunal species richness in once completely cleared regenerating forest was on average 13% (±9.8) lower than historically selectively logged forest. The presence of the small unmarked road significantly altered levels of faunal biodiversity for three taxa, up to and potentially beyond 350m into the forest interior. Most notably, the impact on biodiversity extended to at least 32% of the whole reserve area. The assessment of butterflies across strata showed that different vertical zones within the same rainforest responded differently in areas with different historic human disturbance. A comparison between forest regenerating after selective logging and forest regenerating after complete clearance, showed that there was a 17% greater reduction in canopy species richness in the historically cleared forest compared with the terrestrial community. Comparing arboreal camera traps with traditional ground-based techniques suggests that camera traps are an effective tool for inventorying secretive arboreal rainforest mammal communities and detect a higher number of cryptic species. Finally, the two survey methodologies used to assess amphibian communities identified contrasting biodiversity patterns in a human modified rainforest; one indicated biodiversity differences between forests with different human disturbance histories, whereas the other suggested no differences between forest disturbance types. Overall, in this thesis I find that the conservation and biodiversity value of regenerating and human disturbed tropical forest can potentially contribute to rainforest biodiversity conservation, particularly in the best of circumstances. I also highlight the importance of utilising appropriate study methodologies that to investigate these three-dimensional habitats, and contribute to the development of methodologies to do so. However, care should be taken when using different survey methodologies, which can provide contrasting biodiversity patterns in response to human disturbance.
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As passagens em grelha são infra-estruturas largamente utilizadas para impedir a deslocação do gado, mas que permitem a circulação de viaturas. Porém, também resultam numa armadilha de fosso onde pequenos animais terrestres podem cair inadvertidamente. O principal objectivo deste estudo foi verificar o efeito que as passagens em grelha têm sobre as populações de anfíbios, aquando das suas deslocações sazonais. Estudaram-se 18 passagens em grelha localizadas em duas zonas de amostragem - Elvas e Alandroal - no Alto Alentejo (Portugal). Esta investigação revelou que a principal espécie encarcerada nestas infra-estruturas é o sapo-de-unha-negra (Pelobates cultripes). Em termos gerais, os anfíbios mais terrestres são significativamente (teste do x2) mais afectados do que os anfíbios marcadamente aquáticos. O teste de Mantel mostrou que não existe correlação entre o tipo de passagem em grelha e os anfíbios encontrados nessas infra-estruturas. Para mitigar o aprisionamento de anfíbios nas passagens em grelha, são propostas cinco medidas. ABSTRACT; Cattle grids are infrastructures widely used to avoid the movement of cattle along a road, though allowing the circulation of vehicles. However, they also result in a pit trap where small terrestrial animals may inadvertently fall. The main objective of this study was to check the effect that cattle grids have on amphibian populations, during their seasonal migrations. 18 cattle grids, located in two sampling zones - Elvas and Alandroal- in Alto Alentejo (Portugal), were studied. This investigation showed that the main species imprisoned in these devices is the iberian spadefoot toad (Pelobates cultripes). Generally, the more terrestrial amphibians are significantly (x2 test) more affected than markedly aquatic amphibians. Mantel test showed that there is no correlation between different kinds of cattle grids and the amphibians found in these infrastructures. To mitigate the imprisonment of amphibians in cattle grids, five measures are proposed.
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As rodovias podem contribuir para a diminuição de populações de anfíbios de várias formas, sendo a mais visível a mortalidade por atropelamento. Neste trabalho procurou-se observar a forma como o tráfego pode afectar a mortalidade de anfíbios. A recolha de dados foi efectuada em duas estradas rurais próximas onde foram registadas as espécies observadas e se estas estavam vivas ou mortas, entre outros. Os resultados comprovaram não haver diferenças significativas em relação ao número de indivíduos ou à proporção das espécies que atravessam as vias e confirmaram que uma das estradas possui uma percentagem de mortalidade muito superior à outra. Os testes estatísticos também revelaram existir uma diferença significativa entre o tráfego nas duas estradas. Desta forma, na estrada com mais trânsito foi observado um número muito superior de mortos. Foi, portanto, possível relacionar os resultados e concluir que os anfíbios são negativamente afectados pela intensidade do trânsito rodoviário. ABSTRACT; The roads can contribute to the amphibian populations decline in many ways, being the most visible the roadkills. The purpose of this study was to observe how the traffic can affect the amphibian mortality. The data collection was conducted in two rural roads, near to each other, where the species observed were recorded, and if they were alive or dead, among other information. The results showed no significant differences in the number of individual or in the proportion of species that cross the roads and confirmed that one of the road has a much higher mortality percentage than the other. Statistical tests also revealed a significant difference between the traffic of the two roads. Thus, on the road with more traffic was observed a much higher number of deaths. It was therefore possible to relate the results and conclude that the amphibians are negatively affected by the traffic intensity.
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As the number of fungal pathogen outbreaks become more frequent worldwide across taxa, so have the number of species extirpations and communities persisting with the pathogen. This phenomenon raises questions, such as: “what leads to host extinction during an outbreak?” and “how are hosts persisting once the pathogen establishes?.” But the data on host populations and communities across life stages before and after pathogen arrival rarely exist to answer these questions. Over the past three to four decades, the amphibian-killing fungus Batrachochytrim dendrobatidis (Bd) spread in a wave-like manner across Central America, leading to rapid species extirpations and population declines. I collected data on tadpole and adult amphibians in El Copé, Panama before, during, and after the Bd outbreak to answer these questions. I used Bayesian statistical approaches to account for imperfect host and pathogen detection of marked and unmarked individuals. In the tadpole community, within 11 months of Bds arrival, density and occupancy rapidly declined. Species losses were phylogenetically correlated, with glass frogs disappearing first, and tree frogs and poison-dart frogs remaining. I found that tadpole communities resembled one another more strongly after the outbreak than they did before Bd invasion. I found no tadpoles within 22 months of the outbreak and limited signs of recovery within 10 years. In contrast, at the same site, for a population of male glass frogs, Espadarana prosopleon, I found that 10 years post-outbreak, the population was consistently half its historic abundance, and that the lack of recruits to the population explained why the population had not rebounded, rather than high pathogen-induced mortality. And finally, examining the entire amphibian community, I found high pathogen prevalence, low infection intensities, and high survival rates of uninfected and infected hosts. Bd transmission risk, i.e., the probability a susceptible host becomes infected, did not relate to host density, pathogen prevalence, or infection intensity– Bd transmission risk was uniform across the study area. My results are especially relevant to conservation biologists aiming to predict the future impacts of Bd outbreaks, those trying to manage persisting populations, and those interested in reintroducing species back into wild amphibian communities.
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Tese (doutorado)—Universidade de Brasília, Instituto de Ciências Biológicas, Programa de Pós-Graduação em Biologia Molecular, 2015.
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Doutoramento em Engenharia Florestal e dos Recursos Naturais - Instituto Superior de Agronomia - UL
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Dissertação de mest. em Gestão e Conservação da Natureza, Faculdade de Ciências do Mar e do Ambiente, Univ. do Algarve, 2004
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BACKGROUND Herpesvirus can infect a wide range of animal species: mammals, birds, reptiles, fish, amphibians and bivalves. In marine mammals, several alpha- and gammaherpesvirus have been identified in some cetaceans and pinnipeds species. To date, however, this virus has not been detected in any member of the Balaenoptera genus. CASE PRESENTATION Herpesvirus was determined by molecular methods in tissue samples from a male fin whale juvenile (Balaenoptera physalus) and a female common minke whale calf (Balaenoptera acutorostrata) stranded on the Mediterranean coast of the Region of Valencia (Spain). Samples of skin and penile mucosa from the fin whale and samples of skin, muscle and central nervous system tissue from the common minke whale tested positive for herpesvirus based on sequences of the DNA polymerase gene. Sequences from fin whale were identical and belonged to the Alphaherpesvirinae subfamily. Only members of the Gammaherpesvirinae subfamily were amplified from the common minke whale, and sequences from the muscle and central nervous system were identical. Sequences in GenBank most closely related to these novel sequences were viruses isolated from other cetacean species, consistent with previous observations that herpesviruses show similar phylogenetic branching as their hosts. CONCLUSIONS To our knowledge, this is the first molecular determination of herpesvirus in the Balaenoptera genus. It shows that herpesvirus should be included in virological evaluation of these animals.
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Polychlorinated biphenyls (PCBs) and substituted phenylamine antioxidants (SPAs) are two chemical groups that have been used in multiple Canadian industrial processes. Despite the production ban of PCBs in North America in 1977, they are still ubiquitous in the environment and in wildlife tissues. Previous studies of fish, amphibians, birds, and mammals have shown that PCBs are toxic and act as endocrine disruptors. In contrast, SPAs, specifically N-phenyl-1-naphthylamine (PANA), have received very little attention despite their current use in Canada and their expected environmental releases. The effects of PCB and PANA exposures in reptiles remain unknown thus, juvenile Chelydra serpentina were used in this thesis as a model vertebrate to fill in missing toxicity research gaps due to their importance as an environmental indicator. First, food pellets were spiked at an environmentally relevant concentration of the PCB mixture Aroclor 1254 (A1254) to model hepatic bioaccumulation (0.45 μg/g A1254 for 31 days) and depuration (clean food for 50 days) of PCBs in turtles. No significant differences in PCB concentrations were observed between the control and treated animals, suggesting that juvenile turtles exposed to environmentally relevant concentrations of PCBs can likely detoxify low concentrations of PCBs. Additionally, two dose-response experiments were performed using A1254 or PANA spiked food (0-12.7 μg/g and 0-3,446 μg/g, respectively) to determine hepatic toxicity and bioaccumulation in juvenile C. serpentina. An increase in hepatic cyp1a was observed when exposed to the highest dose of both chemicals: 1) for A1254, induction correlated to the significant increase in hepatic PCB congeners that are known to be metabolized by CYP1A; and 2) for PANA, induction suggested that CYP1A has a potential role in its detoxification. PCBs are known endocrine disruptors, but no significant changes were observed for both thyroid receptors (alpha and beta) or by estrogen and androgen receptors. This lack of response, also noted in the PANA exposure, suggests that C. serpentina is less sensitive to endocrine disruption than other vertebrates. Furthermore, the expression of genes involved in cellular stress was not altered in PCB and PANA exposed animals, supporting the resilience of turtles to oxidative stress. This is the first study to demonstrate the toxicity of PCBs and PANA in C. serpentina, demonstrating the turtle’s high tolerance to contamination.
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Disruptive colouration is a visual camouflage composed of false edges and boundaries. Many disruptively camouflaged animals feature enhanced edges; light patches are surrounded by a lighter outline and/or a dark patches are surrounded by a darker outline. This camouflage is particularly common in amphibians, reptiles and lepidopterans. We explored the role that this pattern has in creating effective camouflage. In a visual search task utilising an ultra-large display area mimicking search tasks that might be found in nature, edge enhanced disruptive camouflage increases crypsis, even on substrates that do not provide an obvious visual match. Specifically, edge enhanced camouflage is effective on backgrounds both with and without shadows; i.e. this is not solely due to background matching of the dark edge enhancement element with the shadows. Furthermore, when the dark component of the edge enhancement is omitted the camouflage still provided better crypsis than control patterns without edge enhancement. This kind of edge enhancement improved camouflage on all background types. Lastly, we show that edge enhancement can create a perception of multiple surfaces. We conclude that edge enhancement increases the effectiveness of disruptive camouflage through mechanisms that may include the improved disruption of the object outline by implying pictorial relief.
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Currently, the identification of two cryptic Iberian amphibians, Discoglossus galganoi Capula, Nascetti, Lanza, Bullini and Crespo, 1985 and Discoglossus jeanneae Busack, 1986, relies on molecular characterization. To provide a means to discern the distributions of these species, we used 385-base-pair sequences of the cytochrome b gene to identify 54 Spanish populations of Discoglossus. These data and a series of environmental variables were used to build up a logistic regression model capable of probabilistically designating a specimen of Discoglossus found in any Universal Transverse Mercator (UTM) grid cell of 10 km × 10 km to one of the two species. Western longitudes, wide river basins, and semipermeable (mainly siliceous) and sandstone substrates favored the presence of D. galganoi, while eastern longitudes, mountainous areas, severe floodings, and impermeable (mainly clay) or basic (limestone and gypsum) substrates favored D. jeanneae. Fifteen percent of the UTM cells were predicted to be shared by both species, whereas 51% were clearly in favor of D. galganoi and 34% were in favor of D. jeanneae, considering odds of 4:1. These results suggest that these two species have parapatric distributions and allow for preliminary identification of potential secondary contact areas. The method applied here can be generalized and used for other geographic problems posed by cryptic species.
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The assessment of the habitat condition is the first step of conservation actions and several tools are available to assess wetlands. However, only a few tools are adapted to the priority habitat Mediterranean temporary ponds. Thus, our objectives were (i) to identify biological indicators associated with the different conservation status of Mediterranean tem- porary ponds and (ii) to create an efficient evaluation tool for non-experts using indicators of conservation status. A total of 87 ponds were sampled in southwest Portugal to assess the presence of plants, large branchiopods, amphibians, threatened voles and bats. Ponds with favourable conservation status showed higher species richness of plants, large branchiopods and amphibians. We identified eighteen indicators for favourable ponds: 15 plants, one large branchiopod and two amphibian taxa. We propose a new tool to assess the conservation status of Mediterranean tem- porary ponds based on the presence of these indicators. This tool is an alternative to other common, but time- consuming, methods and can be readily used by trained practitioners. The replication and adaptation of this tool to other regions and habitats enables the collection of comparable data and the geographical scaling-up of the assessments.