993 resultados para Group Package Tour


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The Drought Monitoring workshop of October 1996, held at the Jarvis Leyland Hotel in Preston, England, established 4 priority issues for dealing with the question: How do we monitor the environment to pick up unexpected change ? 1. Review existing data, and review related study areas throughout the country. 2. Modelling and analysis of data 3. Monitoring / new data / sentinel species' 4. Public relations / Promotion. A group was set up to review issue 1 and feedback to the main group. This report establishes this feedback to the group and refers to existing data / monitoring, other Regional and national work, external Organisations and Recommendations. Appendix 1, is a summary of work completed at the workshop.

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EXECUTIVE SUMMARY: At present, the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) criteria used to assess whether a population qualifies for inclusion in the CITES Appendices relate to (A) size of the population, (B) area of distribution of the population, and (C) declines in the size of the population. Numeric guidelines are provided as indicators of a small population (less than 5,000 individuals), a small subpopulation (less than 500 individuals), a restricted area of distribution for a population (less than 10,000 km2), a restricted area of distribution for a subpopula-tion (less than 500 km2), a high rate of decline (a decrease of 50% or more in total within 5 years or two generations whichever is longer or, for a small wild population, a decline of 20% or more in total within ten years or three generations whichever is longer), large fluctuations (population size or area of distribution varies widely, rapidly and frequently, with a variation greater than one order of magnitude), and a short-term fluctuation (one of two years or less). The Working Group discussed several broad issues of relevance to the CITES criteria and guidelines. These included the importance of the historical extent of decline versus the recent rate of decline; the utility and validity of incorporating relative population productivity into decline criteria; the utility of absolute numbers for defining small populations or small areas; the appropriateness of generation times as time frames for examining declines; the importance of the magnitude and frequency of fluctuations as factors affecting risk of extinction; and the overall utility of numeric thresh-olds or guidelines.

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Alguns estudos vêm apontando o hipotireoidismo como um fator de risco para depressão; entretanto, esta associação é ainda controversa. Como objetivo o presente estudo estimou a prevalência de sintomas depressivos numa amostra probabilística de mulheres e investigou se existe uma associação entre níveis de TSH e a presença de sintomas depressivos. Conduzimos um estudo transversal de base populacional onde avaliou-se uma amostra de mulheres com 35 anos ou mais anos de idade, residentes no município do Rio de Janeiro (RJ), que foram entrevistadas e tiveram amostras de sangue coletadas. O desenho de amostra proposto para a pesquisa seguiu um modelo de amostragem probabilística por conglomerado, em três estágios de seleção, tendo por base os setores censitários do município. A função tireoidiana foi medida pelo TSH sérico, a partir das amostras coletadas no domicílio. Para avaliação da presença/ausência de sintomas depressivos utilizou-se um instrumento padronizado e validado (PRIME-MD). Foram também coletados dados sócio demográficos e outras informações de saúde da participante. A prevalência de sintomas depressivos, frequências e associações foram calculadas levando-se em conta o desenho de amostra complexo, utilizando procedimentos específicos do pacote SAS (versão 9.1). Da amostra de 1500 mulheres, 1298 foram entrevistadas, sendo o percentual de não-resposta igual a 13,5%. A amostra final foi composta por 1249 participantes, onde foi encontrada uma prevalência de sintomas depressivos igual a 45,9%. Em relação aos níveis de TSH, 4,8% da amostra apresentaram-se acima do ponto de corte adotado (≥6,0 mUl/ml). Destas, 61,9% apresentaram sintomas depressivos, contra 44,9% entre as mulheres com TSH<6,0 (p=0,04). A análise ajustada mostrou que mulheres com nível de TSH≥6,0 tiveram uma chance duas vezes maior de apresentarem sintomas depressivos do que aquelas com TSH normal (OR=2,04). Ao excluir da análise as participantes que auto-referiram diagnóstico prévio de doença tireoidiana, a associação entre níveis de TSH e sintomas depressivos perdeu a significância. Concluindo, foi observada alta prevalência de sintomas depressivos na amostra, especialmente entre o grupo com níveis elevados de TSH. Os resultados chamam atenção para a importância de se investigar em pacientes deprimidos a comorbidade tireoidiana.

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Assessment and management of risk is needed for sustainable use of genetically modified aquatic organisms (aquatic GMOs). A computer software package for safely conducting research with genetically modified fish and shellfish is described. By answering a series of questions about the organism and the accessible aquatic ecosystem, a researcher or oversight authority can either identify specific risks or conclude that there is a specific reason for safety of the experiment. Risk assessment protocols with examples involving transgenic coho salmon, triploid grass carp and hybrid tilapia are described. In case a specific risk is identified, the user is led to consider risk management measures, involving culture methods, facilities design and operations management, to minimize the risk. Key features of the software are its user-friendly organization; easy access to explanatory text, literature citations and glossary; and automated completion of a worksheet. Documented completion of the Performance Standards can facilitate approval of a well designed experiment by oversight authorities.

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Belugas, Delphinapterus leucas, groups were videotaped concurrent to observer counts during annual NMFS aerial surveys of Cook Inlet, Alaska, from 1994 to 2000. The videotapes provided permanent records of whale groups that could be examined and compared to group size estimates ade by aerial observers.Examination of the video recordings resulted in 275 counts of 79 whale groups. The McLaren formula was used to account for whales missed while they were underwater (average correction factor 2.03; SD=0.64). A correction for whales missed due to video resolution was developed by using a second, paired video camera that magnified images relative to the standard video. This analysis showed that some whales were missed either because their image size fell below the resolution of hte standard video recording or because two whales surfaced so close to each other that their images appeared to be one large whale. The correction method that resulted depended on knowing the average whale image size in the videotapes. Image sizes were measured for 2,775 whales from 275 different passes over whale groups. Corrected group sizes were calcualted as the product of the original count from video, the correction factor for whales missed underwater, and the correction factor for whales missed due to video resolution (averaged 1.17; SD=0.06). A regression formula was developed to estimate group sizes from aerial observer counts; independent variables were the aerial counts and an interaction term relative to encounter rate (whales per second during the counting of a group), which were regressed against the respective group sizes as calculated from the videotapes. Significant effects of encounter rate, either positive or negative, were found for several observers. This formula was used to estimate group size when video was not available. The estimated group sizes were used in the annual abundance estimates.

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This is the report from the West Cumbria Special Fisheries Advisory Group meeting, which was held on the 25th June, 1982. The report contains sections on the Application by British Nuclear Fuels Limited (BNFL) for a temporary licence to abstract additional quantities from Wastwater, and River Derwent Abstraction (Prescribed Flows). The Fisheries Advisory Committee was part of the Regional Water Authorities, in this case the North West Water Authority. This preceded the Environment Agency which came into existence in 1996.