The giant otter (Pteronura brasiliensis) is an aquatic mammal of the Mustelidae family, endemic to South America. Its original distribution corresponds to the region from the Guyanas to Central-North Argentina, but it is extinct or on the verge of extinction in most of its historical range. Currently, the species is considered endangered by the World Conservation Union (IUCN). Based on its geographic distribution in the South American continent and on some morphological characters, two subspecies were suggested: P. brasiliensis brasiliensis, occurring in the Amazon and Orinoco River Basins, and P. brasiliensis paranensis, in the Paraná and Paraguai River Basins. However, there is no consensus on assuming this subspecies division and no detailed studies have been carried out to elucidate this question. This study aims to evaluate the genetic diversity and population structure of Pteronura brasiliensis along its range in Brazil to check the possibility of the existence of two distinct subspecies using also a reciprocal monophyly criterion. We analyzed the control region, and the Cytochrome b and Cytochrome c Oxidase subunit I genes of the mitochondrial DNA in several giant otter populations from the Amazon and Paraguai River Basins. Analyses have indicated some degree of geographic correlation and a high level of inter-population divergence, although the subspecies division is not highly supported. As we observed strong population structure, we cannot rule out the existence of further divisions shaping the species distribution. The results suggest that a more complex population structure occurs in P. brasiliensis, and the conservation practice should concentrate on preserving all remaining local populations.Keywords: giant otter, mitochondrial DNA, conservation genetics, subspecies. Genética da conservação da ariranha (Pteronura brasiliensis) (Carnivora, Mustelidae) ResumoA ariranha (Pteronura brasiliensis) é um mamífero aquático da família Mustelidae, endêmico da América do Sul. Sua distribuição original se estendia desde as Guianas até o centro-norte da Argentina, mas está extinta ou à beira da extinção na maior parte de sua distribuição histórica. Atualmente a espécie é considerada como ameaçada de extinção pela World Conservation Union (IUCN). Em função de sua distribuição no continente sul-americano e de algumas características morfológicas, duas subespécies foram sugeridas: P. brasiliensis brasiliensis, com ocorrência nas bacias do Amazonas e Orinoco, e P. brasiliensis paranensis, ocorrendo nas bacias dos Rios Paraná e Paraguai. Inexiste, contudo, um consenso sobre a validade da divisão em subespécies e nenhum estudo detalhado foi realizado para elucidar esta questão. Este trabalho tem o objetivo de avaliar a diversidade genética e a estrutura populacional de P. brasiliensis ao longo de sua distribuição no Brasil para verificar a existência de duas subespécies baseando-se também em um critério de monofilia recíproca. A região controle e os genes do Citocromo b e da Subunidade I da Citocromo c Oxidase...
According to the literature, giant otters produce one to six cubs at each gestation, with birth peaks occurring from the end of the flood season to the beginning of the low-water period. With the aim of describing some reproductive parameters of the giant otters living in a hydroelectric lake, 56 field excursions to Balbina Hydroelectric Reservoir, hereafter Balbina Lake, were carried out between September 2001 and September 2010 in order to gather information about cub weight and length, litter size and reproductive period of the species in that area. About 80% of the birth records occurred between September and December, characterized by the receding water season and the beginning of the dry season. The number of cubs per gestation varied from one to three animals (mean = 2; n = 36) and average weight and length of neonates were 316.25 ± 64.21g (n = 4) and 31.75 ± 4.86cm (n = 4), respectively. The reproductive period and the litter size produced by giant otters in Balbina Lake were within the range reported in literature for non-dammed areas, indicating that these reproductive parameters were not changed by the reservoir. The weight of cubs analyzed in the reservoir was in average 35% greater than the weight of captive newborn cubs reported in the literature. However, as the animals here analyzed were healthy, it is reasonable to assume that they represent the weight of free-ranging newborn cubs. Artificial lakes had been reported in the literature as favorable environments for giant otters in Guyana, and the results obtained here seem to corroborate this hypothesis and show the plasticity of the species in its use of different habitats as long as the habitats are inside some category of protection, in this way minimizing additional impacts caused by an intense human occupation of the area. Resumo:De acordo com a literatura, as ariranhas geram de um a seis filhotes a cada gestação, com pico de nascimento das crias entre o final da cheia e início do nível baixo das águas dos rios. Com o objetivo de conhecer alguns parâmetros reprodutivos da ariranha em lagos de hidrelétrica, foram realizadas 56 expedições ao lago de Balbina entre setembro 2001 e setembro 2010 e registradas informações sobre o peso e comprimento de filhotes, tamanho da prole e período reprodutivo da espécie no reservatório da Usina Hidrelétrica de Balbina. Cerca de 80% dos registros de nascimentos ocorreu entre os meses de setembro e dezembro, que correspondem às estações de vazante e início da seca na área de estudo. O número de filhotes por gestação variou de um a três animais (média = 2; n = 36) e o peso e comprimento médios de neonatos foram de 316,25 ± 64,21g (n = 4) e 31,75 ± 4,86cm (n = 4), respectivamente. A semelhança quanto ao período reprodutivo e número de filhotes gerados pelas ariranhas de Balbina quando comparados com áreas não represadas revela que, apesar dos distúrbios ambientais causados pelo represamento, estes aspectos reprodutivos da espécie não foram alterados. O peso dos filhotes analisados no reservatório foi e...
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