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1.
Waste Manag Res ; 34(5): 482-6, 2016 May.
Artículo en Inglés | MEDLINE | ID: mdl-27094694

RESUMEN

The electrical detection of leaks in geomembranes is a method that allows identifying leakage of contaminants in lined facilities (e.g. sanitary landfills, pollutant ponds, etc.). The procedure in the field involves placing electrodes above and below the geomembrane, to generate an electrical current, which in turn engenders an electric potential distribution in the protective layer (generally a clayey soil). The electric potential will be greater in areas with higher current density, i.e. near leaks. In this study, we combined models from the literature to carry out a parametric analysis to identify the variables that most influence the amplitude of the electrical signals produced by leaks. The basic hypothesis is that the electrical conduction phenomena in a liner system could be depicted by a direct current circuit. After determining the value of the current at the leak, we calculated the electric potential distribution according to the model of Darilek and Laine. This enabled analysing the sensitivity of the parameters, which can be useful in the design of landfills and facilitate the location of leaks. This study showed that geomembranes with low electrical resistance (owing to low thickness, low resistivity, or extensive area) can hinder the leak detection process. In contrast, low thickness and high resistivity of the protection layer magnify the leak signal.


Asunto(s)
Modelos Teóricos , Instalaciones de Eliminación de Residuos , Silicatos de Aluminio , Arcilla , Electricidad , Eliminación de Residuos/métodos , Suelo , Contaminantes del Agua
2.
Int J Phytoremediation ; 18(4): 295-307, 2016.
Artículo en Inglés | MEDLINE | ID: mdl-26457927

RESUMEN

This study reports a phytoremediation pot experiment using an open-source program. Unsaturated water flow was described by the Richards' equation and solute transport by the advection-dispersion equation. Sink terms in the governing flow and transport equations accounted for root water and solute uptake, respectively. Experimental data were related to application of Vetiver grass to soil contaminated by metal ions. Sensitivity analysis revealed that due to the specific experimental set-up (bottom flux not allowed), hydraulic model parameters did not influence root water (and contaminant) uptake. In contrast, the results were highly correlated with plant solar radiation interception efficiency (leaf area index). The amounts of metals accumulated in the plant tissue were compared to numerical values of cumulative uptake. Pb(2+) and Zn(2+) uptake was satisfactorily described using a passive model. However, for Ni(2+) and Cd(2+), a specific calibration of the active uptake model was necessary. Calibrated MM parameters for Ni(2+), Cd(2+), and Pb(2+) were compared to values in the literature, generally suggesting lower rates and saturation advance. A parameter (saturation ratio) was introduced to assess the efficiency of contaminant uptake. Numerical analysis, applying actual field conditions, showed the limitation of the active model for being independent of the transpiration rate.


Asunto(s)
Metales/metabolismo , Modelos Biológicos , Poaceae/metabolismo , Contaminantes del Suelo/metabolismo , Biodegradación Ambiental , Raíces de Plantas/metabolismo , Suelo/química
3.
Int J Phytoremediation ; 17(1-6): 242-8, 2015.
Artículo en Inglés | MEDLINE | ID: mdl-25397982

RESUMEN

A finite element code was used for investigating the effect of some relevant characteristics of a phytoremediation project (crop type and density, presence of an irrigation system, soil capping and root depth). The evolution of the plume of contamination of Cd2+, Pb2+, and Zn2+ was simulated taking into account reactive transport and root processes. The plant contaminant uptake model was previously calibrated using data from greenhouse experiments. The simulations adopted pedological and climatological data representative of a sub-tropical environment. Although the results obtained were specific for the proposed scenario, it was observed that, for more mobile contaminants, poor water conditions favor stabilization but inhibit plant extraction. Otherwise an irrigation system that decreases crop water stress had an opposite effect. For less mobile contaminants, the remediation process did not have appreciable advantages. Despite its simplifying assumptions, particularly about contaminant sorption in the soil and plant system, the numerical analysis provided useful insight for the phytoextraction process important in view of field experiments.


Asunto(s)
Cadmio/metabolismo , Chrysopogon/metabolismo , Restauración y Remediación Ambiental/métodos , Plomo/metabolismo , Contaminantes del Suelo/metabolismo , Zinc/metabolismo , Biodegradación Ambiental , Cadmio/química , Chrysopogon/química , Restauración y Remediación Ambiental/instrumentación , Cinética , Plomo/química , Raíces de Plantas/química , Raíces de Plantas/metabolismo , Suelo/química , Contaminantes del Suelo/química , Zinc/química
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