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1.
Water Sci Technol ; 67(1): 217-23, 2013.
Artículo en Inglés | MEDLINE | ID: mdl-23128642

RESUMEN

Wildland fire is an important disturbance factor that can cause severe ecological and watershed damage. Depending on fire severity and watershed extension, reservoir suspended solids concentration (SSC), which arrives through river load, is expected to increase. Satellite remote sensing is an alternative technique to measure SSC in a reservoir. In this paper we evaluate the applicability of multitemporal Landsat data for mapping and monitoring of the SSC in a reservoir whose watershed was exposed to fires. Besides, we aim to identify catchment areas that have been burned, estimating the level of burn severity that occurred because of the fire. The Landsat images were radiometrically, atmospherically and geometrically corrected. Using the differenced normalized burn ratio (dNBR) algorithm, the perimeter and severity of fire was mapped. A theoretical model to characterize the distribution of SSC using multitemporal Landsat data was developed. The relationship between burn severity maps, rainfall and SSC maps improved our understanding of management actions on a reservoir which suffers frequent wildfires on its watershed. The theoretical model here developed may be considered as a low cost measurement tool for water management authorities, particularly when in-situ data are not available.


Asunto(s)
Incendios , Tecnología de Sensores Remotos , Movimientos del Agua , Contaminantes Químicos del Agua/química , Ecosistema , Nave Espacial , Factores de Tiempo
2.
Water Sci Technol ; 66(12): 2722-30, 2012.
Artículo en Inglés | MEDLINE | ID: mdl-23109591

RESUMEN

Artificial thermal mixing of the water column is a common method of addressing water quality problems with the most popular method of destratification being the bubble curtain. The air or oxygen distribution along submerged multiport diffusers is based on similar basic principles as those of outfall disposal systems. Moreover, the disposal of sequestered greenhouse gases into the ocean, as recently proposed by several researchers to mitigate the global warming problem, requires analogous design criteria. In this paper, the influence of a bubble-plume is evaluated using full-scale temperature and water quality data collected in San Roque Reservoir, Argentina. A composite system consisting of seven separated diffusers connected to four 500 kPa compressors was installed at this reservoir by the end of 2008. The original purpose of this air bubble system was to reduce the stratification, so that the water body may completely mix under natural phenomena and remain well oxygenated throughout the year. By using a combination of the field measurements and modelling, this work demonstrates that thermal mixing by means of compressed air may improve water quality; however, if improperly sized or operated, such mixing can also cause deterioration. Any disruption in aeration during the destratification process, for example, may result in a reduction of oxygen levels due to the higher hypolimnetic temperatures. Further, the use of artificial destratification appears to have insignificant influence on reducing evaporation rates in relatively shallow impoundments such as San Roque reservoir.


Asunto(s)
Temperatura , Calidad del Agua , Abastecimiento de Agua , Argentina , Clorofila/análisis , Clorofila A , Simulación por Computador , Geografía , Oxígeno/análisis , Lluvia , Solubilidad , Propiedades de Superficie , Volatilización , Agua/química
3.
Braz J Biol ; 70(3 Suppl): 841-5, 2010 Oct.
Artículo en Inglés | MEDLINE | ID: mdl-21085789

RESUMEN

Piedras Moras reservoir (32° 10'27" S and 64° 16' 29" W; 832 ha), integrates a series of artificial lakes belonging to the Rio Tercero basin (Córdoba, Argentina). During March 2009 an algal bloom occurred, coinciding with several animal species mortality, mainly wild birds. The goal of this work was to establish the trophic status of the reservoir in relation to that mortality. Variables were evaluated in situ (temperature and water transparency) and samples were taken in order to identify algal species, Chl-a concentration (spectrophotometry) and toxins - total microcystines- (inmuno-enzymatic assay, ELISA). Histopathology studies were made on Fulica sp. A strong heterogenity in water transparency was observed, and "patches" of Potamogeton berteroanus distributed all along the lake, with Secchi disk minimal and medium values of 0.15 and 0.94 m. Chl-a concentration oscillated from 35.7 to 320.9 mg.m-3. Predominant phytoplankton species were Anabaena spiroides and Microcystis aeruginosa (Cyanophyceae). Water temperature was 27.8 °C (±0.88). Maximal value of total microcystine concentration was 0.23 µg.L-1. Chl-a concentration at the moment when mass mortality occurred (2.022 mg.m-3), and histopathological observations, strongly suggest that the animals' death was due to cianotoxins.


Asunto(s)
Toxinas Bacterianas/toxicidad , Aves , Cianobacterias , Monitoreo del Ambiente/métodos , Toxinas Marinas/toxicidad , Microcistinas/toxicidad , Mortalidad , Caracoles/efectos de los fármacos , Animales , Argentina , Cianobacterias/clasificación , Toxinas de Cianobacterias , Ensayo de Inmunoadsorción Enzimática , Agua Dulce , Espectrofotometría
4.
Braz. j. biol ; 70(3)Aug. 2010.
Artículo en Inglés | LILACS-Express | LILACS, VETINDEX | ID: biblio-1468043

RESUMEN

Piedras Moras reservoir (32° 10'27" S and 64° 16' 29" W; 832 ha), integrates a series of artificial lakes belonging to the Rio Tercero basin (Córdoba, Argentina). During March 2009 an algal bloom occurred, coinciding with several animal species mortality, mainly wild birds. The goal of this work was to establish the trophic status of the reservoir in relation to that mortality. Variables were evaluated in situ (temperature and water transparency) and samples were taken in order to identify algal species, Chl-a concentration (spectrophotometry) and toxins - total microcystines- (inmuno-enzymatic assay, ELISA). Histopathology studies were made on Fulica sp. A strong heterogenity in water transparency was observed, and "patches" of Potamogeton berteroanus distributed all along the lake, with Secchi disk minimal and medium values of 0.15 and 0.94 m. Chl-a concentration oscillated from 35.7 to 320.9 mg.m-3. Predominant phytoplankton species were Anabaena spiroides and Microcystis aeruginosa (Cyanophyceae). Water temperature was 27.8 °C (±0.88). Maximal value of total microcystine concentration was 0.23 g.L-1. Chl-a concentration at the moment when mass mortality occurred (2.022 mg.m-3), and histopathological observations, strongly suggest that the animals' death was due to cianotoxins.


O reservatório de Piedras Moras (32° 10'27" S e 64° 16' 29" W; 832 ha) faz parte de uma série de lagos artificiais que estão localizados na bacia do rio Tercero (Córdoba, Argentina). Durante março de 2009, ocorreu um florescimento maciço de cianobactérias que resultou na morte de muitas espécies de animais, especialmente aves aquáticas silvestres. O objetivo deste trabalho foi o de estabelecer o estado trófico do reservatório em função desta mortalidade. As variáveis foram avaliadas in situ (temperatura e transparência da água). Foram coletadas amostras para analisar as espécies de algas encontradas nos florescimentos. Foram determinados chl-a (espectrofotometria) e toxinas (microcistinas totais - ensaio imunoenzimático ELISA). Estudos histopalógicos foram realizados em Fulica sp. Uma grande heterogeneidade em transparência de água foi observada e agrupamentos de Potamogeton berteroanus estavam distribuídos em todo o reservatório com valores mínimos e médios do disco de Secchi de 0,15 a 0,54 m. Concentrações de chl-a oscilaram de 35,7 a 320,9 mg.m-3. As espécies fitoplanctônicas dominantes identificadas foram Anabaena spiroides e Microcystis aeruginosa (Cyanophyceae). A temperatura da água foi de 27,8 °C (±0.88). O valor máximo de concentração de microcistinas foi de 0,23 µg.L-1. A concentração de chl-a, quando ocorreu a mortalidade em massa (2,022 mg.m-3), e as lesões histopatológicas indicam que a mortalidade de animais foi devida a cianotoxinas.

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