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Natural and synthesised iron-rich amendments for As and Pb immobilisation in agricultural soil

机译:用于农业土壤中砷和铅固定化的天然和合成富铁修正剂

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The immobilisation of heavy metals in contaminated soils is a promising alternative to conventional remediation techniques. Very few studies have focused on the use of iron-rich nanomaterials and natural materials for the adsorption of toxic metals in soils. Synthesised iron-rich nanomaterials (Fe and Zr-Fe oxides) and natural iron-rich materials (natural red earth; NRE) were used to immobilise As and Pb in contaminated agricultural soil. Total concentrations of As and Pb in the initial soil (as control) were 170.76 and 1945.11 mgkg~(-1), respectively. Amendments were applied into the soil at 1, 2.5 and 5% (w/w) in triplicate and incubated for 150 days. Except for the NRE-amended soil, soil pH decreased from 5.6 to 4.9 with increasing application rates of Fe and Zr-Fe oxides. With addition of Fe and Zr-Fe oxides at 5%, the ammonium acetate (NHO4Ac)-extractable Pb was greatly decreased by 83 and 65% compared with NRE addition (43%). All subjected amendments also led to a decrease in NHCUAc-extractable As in the soils, indicating the high capacity of As immobilisation. Soil amended with NRE showed a lower ratio of cyl9:0 to 18:lω7c, indicating decreased microbial stress. The toxicity characteristic leaching procedure produced results similar to the NHO4AC extraction for As and Pb. The NRE addition is recommended for immobilising heavy metals and maintaining biological soil properties.
机译:将重金属固定在受污染的土壤中是常规修复技术的有希望的替代方法。很少有研究集中于使用富铁纳米材料和天然材料吸附土壤中的有毒金属。合成的富铁纳米材料(Fe和Zr-Fe氧化物)和天然富铁材料(天然红土; NRE)用于将As和Pb固定在受污染的农业土壤中。初始土壤(作为对照)中As和Pb的总浓度分别为170.76和1945.11 mgkg〜(-1)。一式三份地将改良剂以1、2.5和5%(w / w)的形式施用于土壤中,并孵育150天。除NRE改良土壤外,随着Fe和Zr-Fe氧化物的施用量增加,土壤pH从5.6降至4.9。与添加NRE(43%)相比,添加5%的Fe和Zr-Fe氧化物时,醋酸铵(NHO4Ac)可萃取的Pb大大降低了83%和65%。所有进行的修正也导致土壤中NHCUAc可提取的As减少,表明固定化As的能力很高。用NRE改良的土壤显示cyl9:0到18:lω7c的比例较低,表明微生物胁迫降低。毒性特征浸出程序产生的结果类似于NHO4AC萃取As和Pb的结果。建议添加NRE以固定重金属并保持生物土壤的特性。

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