976 resultados para 185-1149
Resumo:
O parasitismo é uma importante força seletiva em populações, assim como a competição e a predação. Os parasitos sanguíneos podem afetar a coloração da plumagem, a seleção sexual e o sucesso reprodutivo em aves. As aves da região Antártica têm sido mencionadas na literatura como livres de hemoparasitos. A Baía do Almirantado, na Ilha Rei George, Península Antártica, é a maior Baía da região, abrigando diferentes espécies de aves durante o período reprodutivo. Dentre elas, estão duas espécies de skuas, as mais frequentes da Antártica, skua-sub-antártica (Catharacta lonnbergi) e skua-polar-do-sul (C. maccormicki) e três espécies de pinguins, pinguim-antártico (Pygoscelis antarctica), pinguim-papua (P. papua) e pinguim-de-adélia (P. adeliae). Skuas e pinguins são aves que se dispersam durante o inverno austral, podendo ser potenciais reservatórios e transmissores de parasitos, embora resultados negativos de hemoparasitos tenham sido encontrados para diversas outras aves marinhas e também para a região Antártica. O objetivo do presente trabalho foi investigar a presença de hemoparasitos em pinguins e skuas antárticos na Baía do Almirantado. Amostras de lâminas de esfregaço sanguíneo e de sangue para análises moleculares de pesquisa de Plasmodium/Haemoproteus foram coletadas em dois períodos reprodutivos, de dezembro de 2010 a março de 2011 e de dezembro de 2011 a fevereiro de 2012. Um total de 185 amostras de aves foram coletadas, incluindo 120 pinguins e 65 skuas. Skuas foram tiveram resultados negativos para hemoparasitos. As três espécies de pinguins foram positivas para Plasmodium/Haemoproteus , via técnica molecular, incluindo dois P. papua,dois P. antarctica etrês P. adeliae. Apenas um indivíduo confirmado positivo pela técnica molecular, pertencente a P. papua, foi positivo utilizando a técnica de esfregaço sanguíneo, com diagnóstico de Plasmodium sp. Não houve diferença significativa entre indivíduos machos e fêmeas das espécies parasitadas, assim como entre adultos e filhotes. As aves parasitadas (n=7), foram categorizadas abaixo do peso (n=5) e acima do peso (n=2). O presente estudo é o primeiro a relatar hemoparasitos na região Antártica e também é o primeiro registro de presença de hemoprotozoários para as três espécies de pinguins analisadas. A ausência de hemoparasitos em aves antárticas tem sido justificada pela ausência de potenciais vetores na região. Portanto, é possível que os pinguins parasitados tenham adquirido a infecção durante a dispersão por ocasião do inverno austral. No entanto, skuas antárticas também são aves migratórias, que podem atingir regiões com potenciais vetores reconhecidos, mas nunca foram diagnosticadas com hemoparasitos, o que foi reforçado pelos resultados negativos do presente estudo. Nesse caso, acredita-se que skuas, podem ter um sistema imune competente ou que a ausência de hemoparasitos nessas aves seja justificada por confinamentos filogenéticos entre parasito-hospedeiro. Entretanto, pouco se sabe sobre a existência de vetores na Antártica, rotas migratórias das aves da região e especificidade parasito-hospedeiro. Os resultados inéditos encontrados no presente estudo devem, portanto, servir como ponto de partida para o entendimento das interações parasito-hospedeiro, de forma a contribuir para a preservação do ambiente antártico.
Resumo:
In 1948, the U.S.S.R. began a global campaign of illegal whaling that lasted for three decades and, together with the poorly managed “legal” whaling of other nations, seriously depleted whale populations. Although the general story of this whaling has been told and the catch record largely corrected for the Southern Hemisphere, major gaps remain in the North Pacific. Furthermore, little attention has been paid to the details of this system or its economic context. Using interviews with former Soviet whalers and biologists as well as previously unavailable reports and other material in Russian, our objective is to describe how the Soviet whaling industry was structured and how it worked, from the largest scale of state industrial planning down to the daily details of the ways in which whales were caught and processed, and how data sent to the Bureau of International Whaling Statistics were falsified. Soviet whaling began with the factory ship Aleut in 1933, but by 1963 the industry had a truly global reach, with seven factory fleets (some very large). Catches were driven by a state planning system that set annual production targets. The system gave bonuses and honors only when these were met or exceeded, and it frequently increased the following year’s targets to match the previous year’s production; scientific estimates of the sustainability of the resource were largely ignored. Inevitably, this system led to whale populations being rapidly reduced. Furthermore, productivity was measured in gross output (weights of whales caught), regardless of whether carcasses were sound or rotten, or whether much of the animal was unutilized. Whaling fleets employed numerous people, including women (in one case as the captain of a catcher boat). Because of relatively high salaries and the potential for bonuses, positions in the whaling industry were much sought-after. Catching and processing of whales was highly mechanized and became increasingly efficient as the industry gained more experience. In a single day, the largest factory ships could process up to 200 small sperm whales, Physeter macrocephalus; 100 humpback whales, Megaptera novaeangliae; or 30–35 pygmy blue whales, Balaenoptera musculus brevicauda. However, processing of many animals involved nothing more than stripping the carcass of blubber and then discarding the rest. Until 1952, the main product was whale oil; only later was baleen whale meat regularly utilized. Falsified data on catches were routinely submitted to the Bureau of International Whaling Statistics, but the true catch and biological data were preserved for research and administrative purposes. National inspectors were present at most times, but, with occasional exceptions, they worked primarily to assist fulfillment of plan targets and routinely ignored the illegal nature of many catches. In all, during 40 years of whaling in the Antarctic, the U.S.S.R. reported 185,778 whales taken but at least 338,336 were actually killed. Data for the North Pacific are currently incomplete, but from provisional data we estimate that at least 30,000 whales were killed illegally in this ocean. Overall, we judge that, worldwide, the U.S.S.R. killed approximately 180,000 whales illegally and caused a number of population crashes. Finally, we note that Soviet illegal catches continued after 1972 despite the presence of international observers on factory fleets.
Resumo:
The Gulf of Mexico Fisheries Management Council tasked the National Marine Fisheries Service with determining the extent, if any, of loss oft rawlable bottom in the Gulf of Mexico based upon fishing industry concerns. There are approximately 31 million hectares in the 21 shrimp statistical zones in the Gulf, approximately 23 million hectares of waters that are <35 fathoms (where most shrimp trawling effort occurs), and approximately 11 million hectares in zones 10-21, <35f athoms, which were examined. There are 31,338 known hangs, snags, artificial reefs, hazards to navigation, oil rigs, and similar obstructions which cause trawling to be unfeasible in these zones. There are several refuge (i.e. untrawlable) areas associated with the Alabama Artificial Reefs. Conservatively assuming 1 hectare for each known obstruction, coupled with the known area of each refuge, the estimate of total untrawlable bottom in zones 10-21 less than 35 fathoms in the Gulf is 185,953 hectares, or roughly 1.7% of this total trawlable area. Sensitivity analysis demonstrated the robustness of this assumption, with a range of 0.3-4.3% possible. In specific shrimp zones, untrawlable area is much less than 1% except in zones 10 (26%) and 11(2.5%), both of which possess a refuge. Other than the implementation periods of these refugia, no temporal trends were detectable with respect to the amount of untrawlable bottom.
Resumo:
An observer program of the shark drift gillnet fishery off the Atlantic coast of Florida and Georgia was begun in 1993 to define the fishery and estimate bycatch including bottlenose dolphin, Tursiops truncatus, and sea turtles. Boats in the fishery were 12.2-19.8 m long. Nets used were 275-1,800 m long and 3.2-4.1 m deep. Stretched-mesh sizes used were 12.7-29.9 cm. Fishing trips were usually <18 h and occurred within 30 n.mi. of port. Fishing with an observer aboard occurred between Savannah, Ga., and Jacksonville, Fla., and off Cape Canaveral, Fla. Nets were set at least 3 n.mi. offshore. Numbers of boats in the fishery increased from 5 in 1993 to 11 in 1995, but total trips decreased from 185 in 1994 to 149 in 1995. During 1993-95, 48 observer trips were completed and 52 net sets were observed. No marine mammals were caught and two loggerhead turtles, Caretta caretta, were caught and released alive. A total of 9,270 animals (12 shark, 21 teleost, 4 ray, and 1 sea turtle species) were captured. Blacknose, Carcharhinus acronotus; Atlantic sharpnose, Rhizoprionodon terraenovae; and blacktip shark, C. limbatus), were the dominant sharks caught. King mackerel, Scomberomorus cavalIa; little tunny, Euthynnus alleteratus; and cownose ray, Rhinoptera bonasus, were the dominant bycatch species. About 8.4% of the total catch was bycatch. Of the totals, 9.4% of the sharks and 37.3% ofthe bycatch were discarded.
Resumo:
The white shark, Carcharodon carcharias, is considered rare in the Gulf of Mexico; however, recent longline captures coupled with historical landings information suggest that the species occurs seasonally (winter-spring) within this region. We examined a total of seven adult and juvenile white sharks (185-472 em total length) captured in waters off the west coast of Florida. Commercial longline fisheries were monitored for white sharks during all months (1981-94), but this species was captured only from January to April. All white sharks were captured in continental shelf waters from 37 to 222 km off the west coast of Florida when sea surface temperatures ranged from 18.7° to 21.6°C. Depths at capture locations ranged from 20 to 164 m. Fishing gear typically used in Gulf of Mexico offshore fisheries may not be effective at capturing this species, and the apparent rarity of white sharks in this area may be, in part, a function of gear bias.
Resumo:
O objetivo deste trabalho é analisar as práticas de divulgação do EBITDA como métrica de desempenho operacional no gerenciamento de segmentos, no período de 2010 a 2012. Trata-se de um estudo descritivo com abordagem qualitativa e quantitativa dos dados realizada por meio da Análise de Conteúdo das Notas Explicativas e do Relatório da Administração. A amostra objetiva é composta por 260 empresas com situação ativa na BM&FBOVESPA em 2013 e distribuídas entre 20 setores da economia. O ano inicial de pesquisa foi determinado pelo fato de ser o primeiro ano da obrigatoriedade de divulgação das Informações por Segmento conforme o pronunciamento técnico do CPC 22. Inicialmente, foram analisadas 780 notas explicativas. Em seguida, a partir da investigação das divulgações das Informações por Segmento pelo CPC 22 em notas explicativas a amostra de trabalho foi constituída por 185; 198 e 203 entidades, respectivamente, em 2010, 2011 e 2012. Deste modo, foram observados nesses três anos 586 relatórios da administração. Os resultados desta pesquisa demonstram que as práticas de divulgação do EBITDA com métrica de desempenho operacional no gerenciamento de Segmentos possui uma representatividade de evidenciação entre os relatórios financeiros de 18%; 16% e 17% respectivamente em 2010, 2011 e 2012. O relatório financeiro com maior participação na divulgação do EBITDA no gerenciamento de negócios foi o Relatório da Administração com 11% em 2010, 10% em 2011 e 11% em 2012. Conclui-se que, em média, 83% das companhias abertas brasileiras não utilizaram o EBITDA como métrica de desempenho operacional no gerenciamento dos segmentos no período de 2010 a 2012.