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Adsorption of nitrate, phosphate, nickel and lead on soils: Risk of groundwater contamination

机译:土壤吸附硝酸盐,磷酸盐,镍和铅:地下水污染的风险

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Agricultural activities pose a significant risk of groundwater pollution. Indeed, fertilizers and treated wastewater used for irrigation are, in part, responsible for the deterioration of groundwater and surface water quality. In some cases, soil may provide a protective barrier against this pollution, but this depends on the nature of the soil and the contaminant. This work presents the effect of the soil clay content on the retention of four different pollutants in order to evaluate the risk they represent for the groundwater. These contaminants are generated by two main agricultural activities: 1/soil fertilization with phosphate and nitrate fertilizers and 2/irrigation with treated wastewater in which heavy metals such as nickel and lead are persistent. Firstly, the characterization of the sand and clay used in this work was performed and showed a cation exchange capacity of 1.24 and 25 meq/100 g, a specific surface area of 0.12 and 67.98 m(2)/g and a percentage of organic matter of 0.15 and 2% for sand and clay, respectively. The retention isotherms on all pollutants and the Langmuir, Freundlich, Freundlich-Langmuir, Hill and Koble-Corrigan models were applied. All experimental isotherms have been successfully adjusted using the Koble-Corrigan expression. The amounts of nitrates, phosphates, nickel and lead retained by the sandy soil, for an initial pollutant concentration equal to 1 meq/L, were evaluated at 0.29, 3.89, 5.97 and 8.56 mu eq/g respectively. In contact with a soil containing 30% clay, the adsorbed amounts were estimated at 3.55, 15.00, 6.97 and 8.79 mu eq/g for nitrates, phosphates, nickel and lead, respectively. These results mean that the pollutants that pose the greatest risk of groundwater contamination when carried by water through sandy soil are classified as follows lead nickel phosphate nitrate while for a clayey soil, the classification becomes as follows: phosphates lead nickel nitrate.
机译:农业活动构成了地下水污染的重大风险。实际上,用于灌溉的肥料和经过处理的废水是部分负责地下水和地表水质的恶化。在某些情况下,土壤可以为这种污染提供保护屏障,但这取决于土壤和污染物的性质。这项工作提出了土壤粘土含量对四种不同污染物保留的影响,以评估它们为地下水所代表的风险。这些污染物由两个主要的农业活动产生:1 /土壤施肥,磷酸盐和硝酸盐肥料和2 /灌溉,处理废水,其中重金属如镍和铅是持久的。首先,进行在该工作中使用的砂和粘土的表征,并显示阳离子交换能力为1.24和25meq / 100g,比表面积为0.12和67.98m(2)/ g的百分比和有机物质砂和粘土分别为0.15和2%。应用了所有污染物和Langmuir,Freundlich,Freundlich-Langmuir,Hill和Koble-Corrigan模型的保留等温。使用Koble-Colrigan表达式成功调整了所有实验等温。在0.29,3.89,5.97和8.56μSq/ g中评估由含有等于1 meq / L的初始污染物浓度的硝酸盐,磷酸盐,镍和铅的量。在与含有30%粘土的土壤接触的情况下,吸附量分别在3.55,15.00,6.97和8.79μSq/ g中估计硝酸盐,磷酸盐,镍和铅。这些结果意味着在通过砂土携带时构成地下水污染风险最大的污染物被分类如下铅<镍<磷酸盐<硝酸盐,同时粘土土壤,分类变得如下:磷酸盐<铅<镍<硝酸盐。

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