200 resultados para Puma concolor
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A predação de rebanhos domésticos por predadores silvestres é o conflito mais intenso entre seres humanos e animais silvestres por causa do prejuízo econômico. A solução encontrada pelos fazendeiros é o abate do predador, causa principal de mortalidade destes animais ao redor do mundo. Para compreender melhor as variáveis ambientais relacionadas a este conflito na região do Parque Nacional de São Joaquim, SC, Brasil, e entorno, foram visitadas propriedades que registraram a presença de leões-baios (Puma concolor) e propriedades que sofreram perdas para este animal durante o ano de 2004. Informações relacionadas ao manejo utilizado com os rebanhos e com a área da fazenda foram coletadas e analisadas conjuntamente com dados provenientes de geoprocessamento (cobertura florestal, altitude, declividade, distância de corpos hídricos e de estradas) mostrando que o manejo utilizado com os rebanhos na área de estudo potencializa os eventos de predação de rebanhos domésticos pelo felídeo em questão. Melhorias no manejo dos rebanhos e das propriedades, diminuição da caça de animais silvestres e a proteção dos fragmentos florestais são ações que, considerando a regionalidade do conflito, podem reduzir os índices de predação. Agências ambientais federais e estaduais tem papel importante na disseminação de informações a respeito da ecologia dos predadores, fornecendo subsídios para os proprietários melhorarem o manejo de seus rebanhos e propriedades. Órgãos extensionistas devem planejar e implantar programas de apoio com técnicas adequadas de manejo das propriedades visando a conservação do meio ambiente.
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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Pós-graduação em Biotecnologia Animal - FMVZ
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Conservation of large felids is not only about collecting ecological information; it is also about understanding people’s values, beliefs, attitudes and behaviour. The overarching goal of this thesis is to assess the relationship between people and jaguars and pumas. Specifically by contributing to the understanding of public acceptance of big cats, as well as the forces (cognitive and social) that influence people’s acceptability. Self-administered questionnaires (n=326) were applied to rural residents outside two protected areas in the State of Sao Paulo: Intervales and PETAR state parks. Findings showed that the acceptability of killing big cats varied accordingly to attitudinal type (positive and negative). Additionally, acceptability of jaguars and pumas was influenced by existence values, attitudes and park credibility. Human dimensions research helped in understanding the relationship between people and the big cats, highlighting the need, for example, to improve the credibility of the parks in the communities and to decrease the fear of jaguars and pumas.
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Coexistence of sympatric species is mediated by resource partitioning. Pumas occur sympatrically with jaguars throughout most of the jaguar's range but few studies have investigated space partitioning between both species. Here, camera trapping and occupancy models accounting for imperfect detection were employed in a Bayesian framework to investigate space partitioning between the jaguar and puma in Emas National Park (ENP), central Brazil. Jaguars were estimated to occupy 54.1% and pumas 39.3% of the sample sites. Jaguar occupancy was negatively correlated with distance to water and positively correlated with the amount of dense habitat surrounding the camera trap. Puma occupancy only showed a weak negative correlation with distance to water and with jaguar presence. Both species were less often present at the same site than expected under independent distributions. Jaguars had a significantly higher detection probability at cameras on roads than at off-road locations. For pumas, detection was similar on and off-road. Results indicate that both differences in habitat use and active avoidance shape space partitioning between jaguars and pumas in ENP. Considering its size, the jaguar is likely the competitively dominant of the two species. Owing to its habitat preferences, suitable jaguar habitat outside the park is probably sparse. Consequently, the jaguar population is likely largely confined to the park, while the puma population is known to extend into ENP's surroundings. (C) 2011 Deutsche Gesellschaft fur Saugetierkunde. Published by Elsevier GmbH. All rights reserved.
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Los animales silvestres obtienen refugio, hábitat, alimento y agua de la cobertura que les ofrece la vegetación dentro del bosque. En los años 60s, la mayoría de las áreas boscosas de Nandarola fueron deforestadas y usadas en la producción agrícola de granos (frijoles, maíz, arroz) y áreas ganaderas. Los campos fueron recientemente abandonados y están siendo colonizados por un joven bosque secundario (González, 2005). La fauna silvestre también sufre procesos de colonización de las áreas abandonadas, de esta forma, es importante conocer que especies son las primeras en ser parte de esa colonización y evaluar los cambios en composición de las comunidades animales en el tiempo, principalmente porque muchos vegetales dependen de éstos para realizar procesos biológicos y ecológicos tan importantes como lo son la dispersión y la polinización. Hasta el momento se han realizados dos muestreos para el monitoreo de la fauna silvestre en un parche de bosque seco secundario de 3.5 ha en Nandarola, realizándose 17 visitas en el primero (año 2007) y 15 en el segundo (año 2009), distribuidas en ocho meses (octubre-mayo en cada muestreo). El área era agrícola y fue abandonado hace 17 años con fines de convertirlo en área forestal. Para la toma de datos se establecieron seis transectos de 20 x 100 m y seis puntos de conteo de 25 m de radio. Fueron contados e identificados todos los animales silvestres de los grupos mamíferos, aves, reptiles y anfibios mediante la técnica de avistamiento, para los cuales se calculó, se comparó la riqueza, abundancia, diversidad biológica y se describió la composición de especie, la preferencia de hábitat, los hábitos alimenticios y también se determinaron las especies de probable ocurrencia en el área de estudio. En promedio entre los dos muestreos fueron determinaron 113 individuos, agrupados en 35 especies, 34 géneros y 26 familias de fauna silvestre. De estas especies cuatro fueron mamíferos, 21 aves, siete reptiles y tres anfibios. Las familias más representadas según el número de especies fueron: Columbidae (3 especies) e Iguanidae (3). Las especies con mayor promedio de abundancia fueron: Campylorynchus rufinucha (22.5 individuos), Thryothorus pleurostictus (11.5), Calocitta formosa (10.5), Turdus grayi (8), Pachyrampuhus aglaiae (7), Eumomota supersiliosa (6.5) y Trogon melanocephalus (6). La abundancia y la riqueza no varió significativamente entre los muestreos, la diversidad fue mayor en el primero, debido al aumento de la dominancia específica (principalmente por Campylorynchus rufinucha ) en el segundo muestreo. El grupo de los mamíferos, reptiles y anfibios fue poco representado en el área de estudio, pudiéndose deber a factores antropogénicos. El paisaje esta mayormente representado por especies de aves de hábitats abiertos y que se alimentan mayoritariamente de invertebrados y semillas. Por otro lado con una relación menos específica los mamíferos y reptiles fueron principalmente de hábitats generalistas y mayormente consumidores de frutas, hierbas y vertebrados. Entre las especies de probable ocurrencia en el área de estudio se determinaron: Bufo coccifer, Boa constrictor, Ctenosaura similis, Mabuya unimarginata, Amazilia rutila, Aratinga canicularis, Ciccaba virgata, Crax rubra, Polyborus plancus, Dasypus novencintus, Dasyprocta punctata, Felis pardalis, Felis wiedii, Philander opossum, Nasua narica, Odocoileus virginianus, Procyon lotor, Puma concolor, Sylvilagus sp, Tayassu tajacu, entre otros.
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The pantherine lineage of the cat family Felidae (order: Carnivora) includes five big cats of genus Panthera and a great many midsized cats known worldwide. Presumably because of their recent and rapid radiation, the evolutionary relationship among pantherines remains ambiguous. We provide an independent assessment of the evolutionary history of pantherine lineage using two complete mitochondrial (mt) genes (ND2 and ND4) and the nuclear beta-fibrmogen intron 7 gene, whose utility in carnivoran phylogeny was first explored. The available four mt (ND5, cytb, 12S, and 16SrRNA) and two nuclear (IRBP and TTR) sequence loci were also combined to reconstruct phylogeny of 14 closely related cat species. Our analyses of combined mt data (six genes; approximate to 3750 bp) and combined mt and nuclear data (nine genes; approximate to 6500 bp) obtained identical tree topologies, which were well-resolved and strongly supported for almost all nodes. Monophyly of Panthera genus in pantherine lineage was confirmed and interspecific affinities within this genus revealed a novel branching pattern, with P. tigris diverging first in Panthera genus, followed by P. onca, P. leo, and last two sister species P. pardus and P. uncia. In addition, close association of Neofelis nebulosa to Panthera, the phylogenetic redefinition of Otocolobus manil within the domestic cat group, and the relatedness of Acinonyx jubatus and Puma concolor were all important findings in the resulting phylogenies. The potential utilities of nine different genes for phylogenetic resolution of closely related pantherine species were also evaluated, with special interest in that of the novel nuclear beta-fibrinogen intron 7. (c) 2005 Elsevier Inc. All rights reserved.
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La plantación de pino en Patagonia ha aumentado en las últimas décadas, y es escaso el conocimiento de su impacto sobre la biodiversidad, particularmente sobre especies de altos requerimientos de hábitat. Mediante trampas cámara se estudiaron cambios en el uso de hábitat de carnívoros en vegetación de ecotono estepa-bosque respecto a plantaciones, y a otras estructuras del paisaje forestado, como cortafuegos, remanentes de vegetación nativa, y plantaciones ralas. Para explorar las diferencias en el uso del hábitat, se caracterizó el mismo a distintas escalas espaciales y se determinó la abundancia recursos tróficos. Se registraron cuatro especies: 1) Gato montés (Leopardus geoffroyi), fue registrado en vegetación nativa, cortafuegos y remanentes de vegetación nativa, pero no en plantaciones; estuvo correlacionado negativamente con la cobertura y densidad arbórea y positivamente con la abundancia de liebre. 2) Zorro colorado (Lycalopex culpaeus) y 3) zorrino (Conepatus chinga), fueron más abundantes en vegetación nativa que en plantaciones, y dentro del paisaje forestado prefirieron plantaciones ralas y cortafuegos. Ambas se asociaron positivamente a la cobertura de vegetación nativa, y el zorro también se asoció positivamente a la abundancia de liebre y riqueza herbácea. 4) Puma (Puma concolor) utilizó en similar medida todos los tipos de hábitat; y se asoció positivamente con la abundancia de jabalí y cobertura de plantación a escala de paisaje. En conclusión, las plantaciones desencadenan cambios en los distintos niveles tróficos de la comunidad, afectando a las presas nativas y favoreciendo a las exóticas, lo cual repercute de distinta manera sobre los carnívoros. A pesar de que gran parte de las especies se ven afectadas en alguna medida, los resultados indican que mediante prácticas de manejo y diseños de paisaje es posible mejorar significativamente la calidad del hábitat, de modo de hacer compatible la actividad forestal con la conservación de la fauna
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La plantación de pino en Patagonia ha aumentado en las últimas décadas, y es escaso el conocimiento de su impacto sobre la biodiversidad, particularmente sobre especies de altos requerimientos de hábitat. Mediante trampas cámara se estudiaron cambios en el uso de hábitat de carnívoros en vegetación de ecotono estepa-bosque respecto a plantaciones, y a otras estructuras del paisaje forestado, como cortafuegos, remanentes de vegetación nativa, y plantaciones ralas. Para explorar las diferencias en el uso del hábitat, se caracterizó el mismo a distintas escalas espaciales y se determinó la abundancia recursos tróficos. Se registraron cuatro especies: 1)Gato montés (Leopardus geoffroyi), fue registrado en vegetación nativa, cortafuegos y remanentes de vegetación nativa, pero no en plantaciones; estuvo correlacionado negativamente con la cobertura y densidad arbórea y positivamente con la abundancia de liebre. 2)Zorro colorado (Lycalopex culpaeus)y 3)zorrino (Conepatus chinga), fueron más abundantes en vegetación nativa que en plantaciones, y dentro del paisaje forestado prefirieron plantaciones ralas y cortafuegos. Ambas se asociaron positivamente a la cobertura de vegetación nativa, y el zorro también se asoció positivamente a la abundancia de liebre y riqueza herbácea. 4)Puma (Puma concolor)utilizó en similar medida todos los tipos de hábitat; y se asoció positivamente con la abundancia de jabalí y cobertura de plantación a escala de paisaje. En conclusión, las plantaciones desencadenan cambios en los distintos niveles tróficos de la comunidad, afectando a las presas nativas y favoreciendo a las exóticas, lo cual repercute de distinta manera sobre los carnívoros. A pesar de que gran parte de las especies se ven afectadas en alguna medida, los resultados indican que mediante prácticas de manejo y diseños de paisaje es posible mejorar significativamente la calidad del hábitat, de modo de hacer compatible la actividad forestal con la conservación de la fauna
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Habitat conversion and environmental degradation have reached alarming levels in the Pantanal, endangering all its biodiversity. This scenario is complicated by the fact that the biome relies on only a few protected areas, which combined do not exceed 10% of the territory. Felids, as predators, play a vital role in the maintenance of this ecosystem, but require large areas, have low population densities and, typically, are very sensitive to environmental disturbances. Amolar Mountain Ridge is considered an area of extreme importance and high priority for conservation within the biome. There are four species of felids in this region: the jaguar (Panthera onca), the puma (Puma concolor), the ocelot (Leopardus pardalis), and jaguarundi (Puma yagouaroundi). However, little is known about the ecology of these species in this region or the magnitude of interaction between the communities living around the protected areas and the animals. The goal of this study was to increase our knowledge about these felids and understand how people interact with them in order to contribute to their conservation in the network of parks within Amolar. Camera trapping surveys were carried out in two areas of the network, covering approximately 83,000 hectares, in order to identify the species of mammals occurring in the region, those that may be potential prey for the felids, and to obtain basic ecological data about both felids and prey. In addition, we conducted surveys in three riverside schools in order to assess the knowledge, perceptions and attitudes of schoolchildren regarding the four focal felids, and surveys among the adult population to assess their perceptions and attitudes towards the jaguar. We recorded a total of 33 species of mammals from both study areas. The large cats were cathemeral, reflecting the temporal activity of larger prey, whereas the ocelot was nocturnal, mirroring the activity of smaller prey. Jaguar occupancy was influenced by prey abundance, while puma occupancy was influenced by patch density in drier dense forest. Jaguars and pumas may be competitors over temporal and spatial scales, while no resource overlap was found for ocelots. Overall, both adults and children tended to have negative perceptions about the cats, which were related to the fear of being attacked. To increase awareness about the species and to maximize the effectiveness of protective measures in the network of reserves, it is recommended to develop and implement an Environmental Educational Program in the medium- to long-term in order to minimize the fear of these felids and to counsel locals on the role of felids in the maintenance of the Pantanal’s biodiversity.
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The use of scat surveys to obtain DNA has been well documented in temperate areas, where DNA preservation may be more effective than in tropical forests. Samples obtained in the tropics are often exposed to high humidity, warm temperatures, frequent rain and intense sunlight, all of which can rapidly degrade DNA. Despite these potential problems, we demonstrate successful mtDNA amplification and sequencing for faeces of carnivores collected in tropical conditions and quantify how sample condition and environmental variables influence the success of PCR amplification and species identification. Additionally, the feasibility of genotyping nuclear microsatellites from jaguar (Panthera onca) faeces was investigated. From October 2007 to December 2008, 93 faecal samples were collected in the southern Brazilian Amazon. A total of eight carnivore species was successfully identified from 71% of all samples obtained. Information theoretic analysis revealed that the number of PCR attempts before a successful sequence was an important negative predictor across all three responses (success of species identification, success of species identification from the first sequence and PCR amplification success), whereas the relative importance of the other three predictors (sample condition, season and distance from forest edge) varied between the three responses. Nuclear microsatellite amplification from jaguar faeces had lower success rates (15-44%) compared with those of the mtDNA marker. Our results show that DNA obtained from faecal samples works efficiently for carnivore species identification in the Amazon forest and also shows potential for nuclear DNA analysis, thus providing a valuable tool for genetic, ecological and conservation studies.
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Sao Paulo is the most developed state in Brazil and little of its native vegetation remains. In Luiz Antonio and Santa Rita do Passa Quatro municipalities, only small fragments of cerrado (Brazilian savanna) physiognomies (cerrado, cerrado sensu stricto) and of semideciduous forest have been left, surrounded by eucalyptus silviculture and sugar-cane agriculture. However, that vegetation mosaic still shelters large mammals, including several carnivore species. To detect the carnivores present in such a mosaic area (50,000 ha), and to find out how they use the landscape, we recorded them through 21 camera traps and 21 track plots, during 18 months. Species richness, diversity and relative frequency were evaluated according to the habitat. Ten species were recorded, some of them locally threatened to extinction (Puma concolor, Leopardus pardalis, Chrysocyon brachyurus). Species diversity did not significantly differ among fragments, and although most species preferred one or another habitat, the carnivore community as a whole explored all the study area regardless of the vegetation cover;eucalyptus plantations were as used by the carnivores as the native fragments. Therefore, it seems possible to maintain such animals in agricultural landscapes, where some large native fragments are left and the matrix is permeable to native fauna.
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So Paulo is the most developed state in Brazil and contains few fragments of native ecosystems, generally surrounded by intensive agriculture lands. Despite this, some areas still shelter large native animals. We aimed at understanding how medium and large carnivores use a mosaic landscape of forest/savanna and agroecosystems, and how the species respond to different landscape parameters (percentage of landcover and edge density), in a multi-scale perspective. The response variables were: species richness, carnivore frequency and frequency for the three most recorded species (Puma concolor, Chrysocyon brachyurus and Leopardus pardalis). We compared 11 competing models using Akaike`s information criterion (AIC) and assessed model support using weight of AIC. Concurrent models were combinations of landcover types (native vegetation, ""cerrado"" formations, ""cerrado"" and eucalypt plantation), landscape feature (percentage of landcover and edge density) and spatial scale. Herein, spatial scale refers to the radius around a sampling point defining a circular landscape. The scales analyzed were 250 (fine), 1,000 (medium) and 2,000 m (coarse). The shape of curves for response variables (linear, exponential and power) was also assessed. Our results indicate that species with high mobility, P. concolor and C. brachyurus, were best explained by edge density of the native vegetation at a coarse scale (2,000 m). The relationship between P. concolor and C. brachyurus frequency had a negative power-shaped response to explanatory variables. This general trend was also observed for species richness and carnivore frequency. Species richness and P. concolor frequency were also well explained by a second concurrent model: edge density of cerrado at the fine (250 m) scale. A different response was recorded for L. pardalis, as the frequency was best explained for the amount of cerrado at the fine (250 m) scale. The curve of response was linearly positive. The contrasting results (P. concolor and C. brachyurus vs L. pardalis) may be due to the much higher mobility of the two first species, in comparison with the third. Still, L. pardalis requires habitat with higher quality when compared with other two species. This study highlights the importance of considering multiple spatial scales when evaluating species responses to different habitats. An important and new finding was the prevalence of edge density over the habitat extension to explain overall carnivore distribution, a key information for planning and management of protected areas.