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利用硫酸亚铁铵使污染土壤中的六价铬钝化的可行性。

Feasibility of using ammonium iron (II) sulphate to passivate hexavalent chromium in polluted soil.

机构信息

Henan Provincial Engineering Research Center of Green Anticorrosion Technology for Magnesium Alloys, College of Chemistry and Chemical Engineering, Henan University, Kaifeng, People's Republic of China.

Henan Engineering Research Center for Control and Remediation of Soil Heavy Pollution, Kaifeng, People's Republic of China.

出版信息

Environ Technol. 2022 Apr;43(10):1522-1531. doi: 10.1080/09593330.2020.1841305. Epub 2020 Nov 11.

Abstract

The use of ammonium iron (II) sulphate ((NH)Fe(SO)) to remediate soil contaminated with Cr (VI) was assessed. (NH)Fe(SO) effectively remediated soil contaminated with Cr (VI) and, acted as a fertilizer by supplying nitrogen because it contains ammonium. The effects of the (NH)Fe(SO) dose, water content, pH of the soil and the contact time were investigated. The amount of Cr (VI) leached from the most-polluted soil, determined using a leaching toxicity procedure using optimized conditions, was 347.64 mg kg when the soil was untreated and 6.74 mg kg when the soil was treated with (NH)Fe(SO). Bio-utilizable Cr contributed 59.44% and 0.16% of the total Cr contents of the untreated and treated soil, respectively. The relatively stable Cr species contributed 24.92% and 98.38% of the total Cr contents of the untreated and treated soil, respectively. The results indicated that adding (NH)Fe(SO) markedly decreased the risk of Cr being released from heavily contaminated soil by decreasing the availability of Cr in the soil. Overall, the results indicated that adding (NH)Fe(SO) causes some Cr (VI) in contaminated soil to be reduced to Cr (III), and to form a precipitate, which decreases the risk of Cr being released. (NH)Fe(SO) can be applied to soil contaminated with Cr (VI) on a large scale because it is cheap and simple to achieve.

摘要

使用硫酸亚铁铵((NH)Fe(SO))来修复受六价铬(Cr (VI))污染的土壤。(NH)Fe(SO) 有效地修复了受 Cr (VI)污染的土壤,并通过提供氮作为肥料,因为它含有铵。研究了(NH)Fe(SO)剂量、水含量、土壤 pH 值和接触时间的影响。在使用优化条件的浸出毒性程序测定最受污染土壤中的 Cr (VI)浸出量时,未处理土壤的浸出量为 347.64 mg kg,而用(NH)Fe(SO)处理的土壤的浸出量为 6.74 mg kg。生物可利用的 Cr 分别占未处理和处理土壤总 Cr 含量的 59.44%和 0.16%。相对稳定的 Cr 物种分别占未处理和处理土壤总 Cr 含量的 24.92%和 98.38%。结果表明,添加(NH)Fe(SO)通过降低土壤中 Cr 的有效性,显著降低了受严重污染土壤中 Cr 释放的风险。总体而言,结果表明,添加(NH)Fe(SO)会导致受污染土壤中的一些 Cr (VI)还原为 Cr (III),并形成沉淀物,从而降低 Cr 释放的风险。由于(NH)Fe(SO)价格便宜且易于实现,因此可大规模应用于受 Cr (VI)污染的土壤。

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