863 resultados para Água - Qualidade


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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

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A deterioração da qualidade da água pode ser causada tanto por resultado da pressão antrópica sobre os ambientes aquáticos em maiores escalas, como por fatores naturais em menores escalas, tal como ocorre em parte da bacia hidrográfica do Rio Arari (Ilha de Marajó, Pará). Este artigo teve como objetivo a avaliação da qualidade das águas superficiais e o estado trófico do Rio Arari, no trecho entre Santana e Cachoeira do Arari, considerando as variações temporais e espaciais de variáveis físicas, químicas e biológicas da água em dois períodos hidrológicos distintos de 2009: descarga máxima (abril e maio) e descarga mínima (setembro e novembro). Os Índices de Qualidade da Água (IQA) e Estado Trófico (IET) foram determinados simultaneamente em amostras de água superficial durante 12 horas consecutivas nas três estações de coleta ao longo do Rio Arari. Os valores do IQA variaram entre "Ruim" e "Regular", e estão provavelmente relacionadas aos elevados níveis de coliformes fecais, baixas concentrações de oxigênio dissolvido e pH ácido do Rio Arari. Conforme o IET, o rio pode ser classificado como supereutrófico e hipereutrófico, reflexo da grande disponibilidade de nutrientes (e.g. fósforo) e elevada biomassa fitoplanctônica em termos de clorofila a. O Rio Arari está sob um processo de eutrofização natural, visto que as fontes de contaminação antrópica ainda são incipientes, mas elas podem contribuir para um processo de longo prazo de eutrofização artificial.

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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

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Pós-graduação em Agronomia (Produção Vegetal) - FCAV

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Pós-graduação em Aquicultura - FCAV

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Pós-graduação em Biometria - IBB

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In order to enable the reuse of the large surplus volume of petroleum produced water for irrigation of crops inedible, the quality evaluation of this water is very important. This work aimed to evaluate the effectiveness of the diffusive gradient in thin films technique (DGT) for the determination of labile Cu (II), Mn (II) and Zn (II) in petroleum produced water destined to reuse in agriculture. Samples were collected at the exit of the wastewater treatment plant (WWTP) (after separation oil/water and flotation) of a Petrobrás onshore production region. Basically, the laboratory experiments with DGT devices involved the evaluation of the behavior of the main variables of the technique for determination of analytes in the samples (diffusion coefficients, immersion time, fractionation of organic and inorganic species, and performance of diffusion gels with different porosities, among others). Also, experiments were conducted based on the solid phase extraction (SPE) protocol with Chelex- 100 resin using previously established protocols to support the study. During the project the possibility of in situ immersions in water treatment plants was evaluated. The DGT technique presented satisfactory results for determination of Mn in produced water, and can be used for in situ determinations. However, the results obtained for Cu and Zn show the need of additional studies

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Aquatic ecosystems are suffering many impacts caused by human activities resulting from the activities occurring around them. With technological progress observed in recent years, this environment has received large amounts of chemicals from industries, agriculture and urban area that affect the aquatic biota. Among these sources of contamination, the oil industry has contributed to the pollution of aquatic environments with both effluents as produced water well as oil spills and their derivatives having toxicity to various organisms. With all the environmental issues has increased concern about water quality and has been used ecotoxicological tests with aquatic organisms to ecosystems to assess the toxicity of chemicals present in the water. In this context the microcrustacea Daphnia similis stands out as a freshwater organism very representative of the aquatic fauna of rivers and high sensitivity to environmental impacts. Thus, the present study aimed to evaluate the lethal toxicity of crude oil and produced water on this microcrustacea. The results showed that the microcrustacea presented high sensitivity to contaminants primarily crude oil. There was also the influence of environmental variables pH and temperature on the survival of organisms

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The work is to study about the quality of surface waters of the Piaguí and neighborhoods Colonia Santa Luzia. Six samples of which the physical, chemical and biological parameters were analyzed were collected. The tests were conducted in accordance with Standard Methods for the Examination of Water and Wastewater 20th edition and compared with the resolution of CONAMA No. 357 (2005). Critical parameters are found in fecal coliform and water coloring, which may indicate an anthropogenic interference in the sampling points (domestic sewage), or the effect of rainfall during the collection period influence the results

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Surface water quality models have been developed since 1925, when Streeter e Phelps created first order equations that represent the balance between DO and BOD. Since then, and specially after the ‘60s, new computational technologies evolved, making it possible to create more complex models, which try to represent, through mathematics, natural phenomena like eutrophication and rivers self-depuration. As main objective of such models is the understanding of aquatic systems and the relationship between them and the environment, so that it can support decision makers in creating water manage plans and in elaborating environmental projects of such resources. Regarding to that, it is of crucial importance the understanding of the models structures, so that one can choose the most appropriate model for the river in question. While one-dimensional models like QUAL2K are more appropriate for long and narrow rivers, bi- or tridimensional models (CE-QUAL-W2, WASP and CEQUAL- ICM) are more commonly used in wide and slower rivers, with higher lateral and/or vertical mixes rates. Besides, the more complex is the river studied more complex the model should be, which demands more costs and time for the model to be applied

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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)