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Assessment of arsenic fractionation, mobility, and bioavailability in mining-affected soils, and remediation measures

机译:评估受采矿影响的土壤中砷的分馏,迁移率和生物利用度,并采取补救措施

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Arsenic (As) concentrations and fractionations were investigated for control and mining-affected soils in Spain, using chemical extraction, column leaching, microbial and cultivation studies. Total As concentrations in all contaminated soils were in the range 96-27 350 mg/kg, demonstrating extremely high concentrations. However, the majority of the plant species accumulated very low As concentrations, while a few plants accumulated relatively high As concentrations (up to 152 mg/kg). Therefore, those plant species that are highly tolerant; grow abundantly in mining-affected areas; and have high biomass and roots, are suitable candidates for the phytostabilization of these contaminated soils. Compared to the total As contents, the very low water-soluble As (0.01-0.71%), sodium acetate (0.3-3.4%), and ammonium-nitrate-extractable As (0.05-0.74% of total As) concentrations and column leaching suggest that the concentrations of readily available As were relatively low in contaminated soils. Single extraction indicated that maximum concentrations of As in these soils were extracted with ammonium oxalate and hydroxylamine hydrochloride, suggesting that the major fraction of As is predominantly bound to poorly crystalline Fe, Mn and Al oxides. The residual fractions (35-80.2% of total As) were bound with silicate minerals. We document here some important results in relation to the role of microbial and cultivation activity: indigenous bacteria can mobilize As from the contaminated soils under changing redox conditions when a source of organic matter is available; and plant cultivation can promote the exchangeable and plant-available As in contaminated soils, indicating the potential risk of environmental and food-chain contamination.
机译:通过化学提取,柱浸,微生物和栽培研究,对西班牙控制和受采矿影响的土壤中砷(As)的浓度和分级进行了研究。所有受污染土壤中的总砷浓度在96-27 350 mg / kg范围内,表明其浓度极高。但是,大多数植物物种积累的砷浓度非常低,而少数植物积累的砷浓度相对较高(高达152 mg / kg)。因此,那些植物具有高度的耐受性。在受采矿影响的地区大量种植;并且具有高生物量和根系,是这些受污染土壤的植物稳定化的合适候选者。与总砷含量相比,极低的水溶性砷(0.01-0.71%),乙酸钠(0.3-3.4%)和硝酸铵可萃取砷(占总砷的0.05-0.74%)浓度和柱浸出这表明在污染的土壤中,易于获得的砷的浓度相对较低。单次萃取表明,用草酸铵和盐酸羟胺萃取了这些土壤中As的最大浓度,这表明As的主要部分主要与弱结晶的Fe,Mn和Al氧化物结合。剩余部分(占总砷的35-80.2%)与硅酸盐矿物结合。我们在这里记录了有关微生物和耕作活动的一些重要结果:当有机物源可用时,在不断变化的氧化还原条件下,土著细菌可以从受污染的土壤中迁移出As;而植物种植可以促进被污染土壤中可交换和可利用的砷,表明环境和食物链污染的潜在风险。

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