953 resultados para Water quality standards


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Many regions of the world, including inland lakes, present with suboptimal conditions for the remotely sensed retrieval of optical signals, thus challenging the limits of available satellite data-processing tools, such as atmospheric correction models (ACM) and water constituent-retrieval (WCR) algorithms. Working in such regions, however, can improve our understanding of remote-sensing tools and their applicabil- ity in new contexts, in addition to potentially offering useful information about aquatic ecology. Here, we assess and compare 32 combinations of two ACMs, two WCRs, and three binary categories of data quality standards to optimize a remotely sensed proxy of plankton biomass in Lake Kivu. Each parameter set is compared against the available ground-truth match-ups using Spearman's right-tailed ρ. Focusing on the best sets from each ACM-WCR combination, their performances are discussed with regard to data distribution, sample size, spatial completeness, and seasonality. The results of this study may be of interest both for ecological studies on Lake Kivu and for epidemio- logical studies of disease, such as cholera, the dynamics of which has been associated with plankton biomass in other regions of the world.

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The Iowa Department of Natural Resources has produced an 4 page article about how to assess Iowa's streams and rivers. How to use ambient monitoring of streams and river in Iowa.

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The Iowa Department of Natural Resources has produced an 4 page article about how to assess Iowa's streams and rivers. How to use ambient monitoring of streams and river in Iowa.

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A report on Iowa Water Monitoring produced by Iowa Department of Natural Resources.

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Water fact sheet for Iowa Department of Natural Resources and the Geological Bureau.

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This fact sheet answers questions such as, is it safe to swim in the water and who is monitoring the beaches in Iowa

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This monthly report from the Iowa Department of Natural Resources is about the water quality management of Iowa's rivers, streams and lakes.

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This monthly report from the Iowa Department of Natural Resources is about the water quality management of Iowa's rivers, streams and lakes.

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This monthly report from the Iowa Department of Natural Resources is about the water quality management of Iowa's rivers, streams and lakes.

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En septiembre del 2009 se evaluó el contenido de trazas de metales en los bancos naturales de Meca-Lozas (Tacna), Tancona y Punta Coles (Moquegua), en un ámbito donde la temperatura fue inferior al patrón estacional y en presencia de Aguas Costeras Frías en toda la columna de agua. Las trazas de cobre, plomo y cadmio contenidos en agua de los tres bancos naturales, no superaron los Estándares de Calidad Ambiental para Conservación del Ambiente Acuático (Grupo 4). Las trazas de cobre, plomo, cadmio y cinc para sedimentos, no superó al Probable Nivel de Efecto estipulado en la Tabla de Protección Costera de los EE UU, a excepción del cobre que superó el estándar en una estación (136,99 μg/g) de Meca-Las Lozas. Sólo las concentraciones traza de cobre en los tres bancos naturales y en los cuerpos eviscerados de caracol negro (Thaisella chocolata), lapa (Fissurella sp.), chanque (Concholepas concholepas) y choro (Aulacomya atra) superaron el límite máximo permisible internacional estipulado por la FAO, siendo la mayor concentración de 1782,27 μg/g en la especie Fissurella sp. muestreada en Meca-Lozas, por lo que se concluye que las especies que bioacumulan más trazas de cobre son Fissurella sp., Thaisella chocolata, Concholepas concholepas y Aulacomya atra.

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Entre abril y octubre 2012, se evaluó la línea costera y las bahías Coishco, El Ferrol, Samanco, Tortuga, Casma, Huarmey y Caleta Culebras y los ríos Santa, Lacramarca, Casma, Culebras, Huarmey y Samanco. Se localizaron valores termohalinos propios de Aguas Costeras Frías (ACF) con influencias de vertidos antropogénicos y variaciones locales del proceso de evaporación. En abril el oxígeno disuelto presentó valores >5,00 mg/L en toda el área a excepción de la bahía Coishco (3,72 mg/L); en octubre la concentración más alta estuvo en Samanco (7,51 mg/L) y la más baja en Huarmey (2,53 mg/L), el pH estuvo en relación directa con el oxígeno. En abril y octubre los agentes contaminantes de sólidos suspendidos totales presentaron valores >30,00 mg/L en las bahías Coishco, El Ferrol y Tortuga, superando lo permitido por los Estándares Nacionales de Calidad Ambiental para Agua, categoría 4. En abril y octubre la calidad de agua en la cuenca baja de los ríos Santa, Lacramarca, Casma, Culebras y Huarmey respecto a la concentración de la demanda bioquímica de oxígeno estuvo dentro de los Estándares Nacionales de Calidad Ambiental para Agua, categoría 4.

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The presence of human adenoviruses in recreational water might cause disease in the population upon exposure. Human adenoviruses detected by PCR could also serve as indicators of the virological water quality. In order to assess the applicability of human adenoviruses to the evaluation of the faecal contamination in European bathing waters, a real-time quantitative PCR assay was developed for the quantification of human adenoviruses in 132 samples collected from 24 different recreational marine and freshwater sites in nine European countries.Selected samples presenting positive nested-PCR results for human adenoviruses were analyzed using quantitative PCR and 80 samples from a total of 132 produced quantitative results with mean values of 3.2x102 10 per 100 ml of water, human adenovirus 41 being the most prevalent serotype. Human adenoviruses were quantified in samples from all 15 surveillance laboratories. Statistical analysis showed no homogeneous linear relation between humanadenoviruses and E. coli, intestinal enterococci or somatic coliphages concentrations in the tested samples when considering all the data together. Significant correlations between human adenoviruses and at least one of the other indicators were observed only when data from individual Laboratories were considered. The quantification of human adenoviruses may provide complementary information in relation to the use of bacterial standards in the control of water quality in bathing water.

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The presence of human adenoviruses in recreational water might cause disease in the population upon exposure. Human adenoviruses detected by PCR could also serve as indicators of the virological water quality. In order to assess the applicability of human adenoviruses to the evaluation of the faecal contamination in European bathing waters, a real-time quantitative PCR assay was developed for the quantification of human adenoviruses in 132 samples collected from 24 different recreational marine and freshwater sites in nine European countries.Selected samples presenting positive nested-PCR results for human adenoviruses were analyzed using quantitative PCR and 80 samples from a total of 132 produced quantitative results with mean values of 3.2x102 10 per 100 ml of water, human adenovirus 41 being the most prevalent serotype. Human adenoviruses were quantified in samples from all 15 surveillance laboratories. Statistical analysis showed no homogeneous linear relation between humanadenoviruses and E. coli, intestinal enterococci or somatic coliphages concentrations in the tested samples when considering all the data together. Significant correlations between human adenoviruses and at least one of the other indicators were observed only when data from individual Laboratories were considered. The quantification of human adenoviruses may provide complementary information in relation to the use of bacterial standards in the control of water quality in bathing water.

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This final report to the Iowa Watershed Improvement Review Board by the City of Remsen Utilities consists of accomplishments made by the Remsen Utilities as per this agreement. The City of Remsen Utilities did in fact purchase approximately 27 acres of land lying upstream of the city’s water well field. The land was purchased from Mr. Larry Rodesch and Mr. Rich Harpenau for the purpose of removing nitrates from Remsen’s water source and establishing native prairie grasses to assist in this removal.

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Water planning efforts typically identify problems and needs. But simply calling attention to issues is usually not enough to spur action; the end result of many well-intentioned planning efforts is a report that ends up gathering dust on a shelf. Vague recommendations like “Water conservation measures should be implemented” usually accomplish little by themselves as they don’t assign responsibility to anyone. Success is more likely when an implementation strategy — who can and should do what — is developed as part of the planning process. The more detailed and specific the implementation strategy, the greater the chance that something will actually be done. The question then becomes who has the legal authority or responsibility to do what? Are new laws and programs needed or can existing ones be used to implement the recommendations? ... This document is divided into four main parts. The first, “Carrots and Sticks” looks at two basic approaches — regulatory and non-regulatory — that can be, and are, used to carry out water policy. Both have advantages and disadvantages that need to be considered. The second, “The powers of federal, state and local governments…,” looks at the constitutional powers the federal government and state and local governments have to carry out water policy. An initial look at the U. S. Constitution might suggest the federal government’s regulatory authority over water is limited but, in fact, its powers are very substantial. States have considerable authority to do a number of things but have to be mindful of any federal efforts that might conflict with those state efforts. And local governments can only do those things the state constitution or state legislature says they can do and must conform to any requirements or limitations on those powers that are contained in the enabling acts. Parts three and four examine in more detail the main programs and agencies at the federal level as well as Iowa’s state and local levels and the roles they play in national and state water policy.