926 resultados para temporary habitats


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Abstract Introduction: Exhaustive and/or unaccustomed exercise, mainly those involving eccentric muscle actions, induces temporary muscle damage, evidenced by Delayed Onset Muscle Soreness. Different strategies to recover the signs and symptoms of this myogenic condition have been studied by researchers, as a result a significant number of articles on this issue have been published. Purpose: A systematic review was conducted to assess the evidence of the physiotherapeutic interventions of exercise-induced muscle damage. Methods: The electronic data bases were searched, including MEDLINE (1996-2011), CINHAL (1982- 2011), EMBASE (1988-2011), PEDro (1950-2011), and SPORTDiscus (1985-2011). Systematic review was limited to randomized control trials (RCTs) studies, written in English or Portuguese, which included physiotherapeutic interventions, namely massage, cryotherapy, stretching and low-intensity exercise, on adult human subjects (18-60 years old) of either gender. Studies were excluded when the intervention could not be assessed independently. The methodological quality of RCTs was independently assessed with the PEDro Scale by three reviewers. Results: Thirty-three studies were included in the systematic review; eight analyzed the effects of the massage, ten analyzed the effects of the cryotherapy, eight the effect of stretching and seventeen focused low-intensity exercise intervention. The results suggest that massage is the most effective intervention and that there is inconclusive evidence to support the use of cryotherapy; whereas the other conventional, namely stretching and low-intensity exercise, there is no evidence to prove their efficacy. Conclusion: The results allow the conclusion that massage is the physiotherapeutic intervention that demonstrated to be the most effective in the relief of symptoms and signs of exercise-induced muscle damage, as a result, massage should still be used in the muscular recovery after sports activities.

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Copyright © 2013 Elsevier Ltd. All rights reserved.

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The hoverfly fauna of the Azores currently comprises 23 species (Smit 2010), but the current state of knowledge concerning these species differs for each island. In the year 1938, R. Frey and R. Storå recorded the first seven hoverfly species on Pico Island (Frey 1945), and these very same ones were still mentioned by Rojo et al. (1997). Smit (2010) added one more species to this list (Table 1). In the summer of 2014, the author of this article sampled hoverflies on Pico Island in several habitats. In this paper, the results will be presented.

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Dissertação apresentada à Escola Superior de Educação de Lisboa para a obtenção do grau de Mestre em Ciências da Educação, especialização em Educação Social e Intervenção Comunitária

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Ocean Science Meeting. Hawaii Convention Center, Honolulu, Hawaii, USA, 23-28 de Fevereiro.

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1st Mares Conference on Marine Ecosystems Health and Conservation. Olhão, Portugal 17-21 November 2014.

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Dissertação apresentada à Escola Superior de Comunicação Social como parte dos requisitos para obtenção de grau de mestre em Audiovisual e Multimédia.

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Tese de Doutoramento em Ciências do Mar, especialidade em Ecologia Marinha.

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Tese de Doutoramento em Ciências do Mar, especialidade em Ecologia Marinha.

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Tese de Doutoramento em Ciências do Mar, especialidade em Ecologia Marinha.

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A presente dissertação tem como intuito aplicar o regime de Responsabilidade Ambiental no perímetro industrial da Monteiro, Ribas – Indústrias, S.A.. Para tal, averiguou-se que na ordem jurídica nacional, o regime de Responsabilidade Ambiental (RA) encontra-se consagrada na legislação nacional pelo Decreto-Lei nº 147/2008 de 29 de Julho (Diploma RA),e respetivas alterações, aplicando-se a danos ambientais ou ameaças iminentes de danos ambientais causados aos recursos naturais nomeadamente “espécies e habitats naturais protegidos”, “água” e “solo”. Também se verificou que este regime introduz obrigações específicas para os operadores abrangidos, designadamente é da responsabilidade do operador aplicar as medidas de prevenção e reparação dos danos, devendo ser reportados os acontecimentos à autoridade competente, Agência Portuguesa do Ambiente. Para cumprimento do requisito da garantia financeira e sendo a Monteiro, Ribas – Indústrias, S.A. enumerada no Anexo III do Decreto-Lei nº 147/2008 de 29 de Julho, optou-se pela constituição de um fundo próprio no valor de 50.000,00€. Com recurso à metodologia proposta pela Norma Espanhola UNE 150008:2008 - Análise e avaliação do Risco Ambiental, procedeu-se à formulação de vários cenários e quantificação de riscos para a Monteiro, Ribas – Indústrias, S.A. tendo-se apurado que os riscos estavam avaliados como baixo ou moderado. Por fim, conclui-se que em Portugal, embora exista um Decreto-Lei sobre Responsabilidade Ambiental, este tema ainda não está suficientemente desenvolvido pois não permite proceder a análise e avaliação do risco ambiental, tendo sido tomado assim como referência a metodologia aplicada na Norma Espanhola UNE 150008:2008.

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A água superficial para posterior consumo humano, tem de passar por diversas etapas de tratamento, de forma a dar cumprimento aos requisitos da legislação vigente, decreto-Lei n.º 306/2007 de 27 de Agosto. Como resultado do referido tratamento produzem-se resíduos, nomeadamente, as lamas de clarificação de água. De acordo com a estratégia da União Europeia, a deposição em aterro destas lamas apenas deverá ser efectuada em situações excepcionais ou temporárias. A procura de uma solução ambientalmente mais aceitável para o destino final a atribuir a estas lamas de clarificação de água deverá ser, um dos objectivos das empresas abastecedoras de água para consumo humano. Com o intuito de verificar a possibilidade de utilização das lamas produzidas nas Estações de Tratamento de Água (ETA) em solos agrícolas, realizaram-se testes ecotoxicológicos para avaliar a capacidade de germinação de sementes de alface (Lactuca sativa). Foram igualmente realizadas determinações de alguns metais nos lixiviados, por espectrofotometria de absorção atómica com atomização por chama e por Câmara de grafite. O cádmio e o chumbo por imposição da legislação aplicável aos géneros alimentícios, Regulamento (CE) 1881/2006 de 19 de Dezembro e o alumínio e o ferro por estarem presentes nos tratamentos de algumas das águas superficiais em estudo. As lamas estudadas eram provenientes de ETA com captação de água superficial em rios e albufeiras distintos do norte de Portugal, com utilização de tratamentos também diferentes. Os resultados obtidos com os lixiviados das lamas provenientes das ETA com captações dos rios Ferreira, Ferro e Vizela e Tâmega, evidenciaram inibição da germinação para algumas das diluições testadas. No entanto, não se observou qualquer efeito tóxico para as lamas das ETA com captações da albufeira do Alto Rabagão e dos rios Rabaçal, Douro e Paiva. Dos metais alumínio, cádmio, ferro e chumbo determinados nos lixiviados, apenas o alumínio estava acima do limite de detecção. No entanto, não foi possível estabelecer qualquer correlação entre o tratamento aplicado à água superficial nas várias ETA com a concentração do alumínio nem com os resultados dos ensaios ecotoxicológicos. Não obstante, parece haver relação entre a proximidade geográfica do local de captação de água e os resultados dos bioensaios.

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The presented work was conducted within the Dissertation / Internship, branch of Environmental Protection Technology, associated to the Master thesis in Chemical Engineering by the Instituto Superior de Engenharia do Porto and it was developed in the Aquatest a.s, headquartered in Prague, in Czech Republic. The ore mining exploitation in the Czech Republic began in the thirteenth century, and has been extended until the twentieth century, being now evident the consequences of the intensive extraction which includes contamination of soil and sub-soil by high concentrations of heavy metals. The mountain region of Zlaté Hory was chosen for the implementation of the remediation project, which consisted in the construction of three cells (tanks), the first to raise the pH, the second for the sedimentation of the formed precipitates and a third to increase the process efficiency in order to reduce high concentrations of metals, with special emphasis on iron, manganese and sulfates. This project was initiated in 2005, being pioneer in this country and is still ongoing due to the complex chemical and biological phenomenon’s inherent to the system. At the site where the project was implemented, there is a natural lagoon, thereby enabling a comparative study of the two systems (natural and artificial) regarding the efficiency of both in the reduction/ removal of the referred pollutants. The study aimed to assist and cooperate in the ongoing investigation at the company Aquatest, in terms of field work conducted in Zlaté Hory and in terms of research methodologies used in it. Thereby, it was carried out a survey and analysis of available data from 2005 to 2008, being complemented by the treatment of new data from 2009 to 2010. Moreover, a theoretical study of the chemical and biological processes that occurs in both systems was performed. Regarding the field work, an active participation in the collection and in situ sample analyzing of water and soil from the natural pond has been attained, with the supervision of Engineer, Irena Šupiková. Laboratory analysis of water and soil were carried out by laboratory technicians. It was found that the natural lagoon is more efficient in reducing iron and manganese, being obtained removal percentages of 100%. The artificial lagoon had a removal percentage of 90% and 33% for iron and manganese respectively. Despite the minor efficiency of the constructed wetland, it must be pointed out that this system was designed for the treatment and consequent reduction of iron. In this context, it can conclude that the main goal has been achieved. In the case of sulphates, the removal optimization is yet a goal to be achieved not only in the Czech Republic but also in other places where this type of contamination persists. In fact, in the natural lagoon and in the constructed wetland, removal efficiencies of 45% and 7% were obtained respectively. It has been speculated that the water at the entrance of both systems has different sources. The analysis of the collected data shows at the entrance of the natural pond, a concentration of 4.6 mg/L of total iron, 14.6 mg/L of manganese and 951 mg/L of sulphates. In the artificial pond, the concentrations are 27.7 mg/L, 8.1 mg/L and 382 mg/L respectively for iron, manganese and sulphates. During 2010 the investigation has been expanded. The study of soil samples has started in order to observe and evaluate the contribution of bacteria in the removal of heavy metals being in its early phase. Summarizing, this technology has revealed to be an interesting solution, since in addition to substantially reduce the mentioned contaminants, mostly iron, it combines the low cost of implementation with an reduced maintenance, and it can also be installed in recreation parks, providing habitats for plants and birds.

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Realization that hard coastal infrastructures support lower biodiversity than natural habitats has prompted a wealth of research seeking to identify design enhancements offering ecological benefits. Some studies showed that artificial structures could be modified to increase levels of diversity. Most studies, however, only considered the short-term ecological effects of such modifications, even though reliance on results from short-term studies may lead to serious misjudgements in conservation. In this study, a sevenyear experiment examined how the addition of small pits to otherwise featureless seawalls may enhance the stocks of a highly-exploited limpet. Modified areas of the seawall supported enhanced stocks of limpets seven years after the addition of pits. Modified areas of the seawall also supported a community that differed in the abundance of littorinids, barnacles andmacroalgae compared to the controls. Responses to different treatments (numbers and size of pits) were speciesspecific and, while some species responded directly to differences among treatments, others might have responded indirectly via changes in the distribution of competing species. This type of habitat enhancement can have positive long-lasting effects on the ecology of urban seascapes.Understanding of species interactions could be used to develop a rule-based approach to enhance biodiversity.