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羟肟酸类铁载体协同浸提重金属-多环芳烃复合污染土壤:阳离子-π 和螯合作用的作用。

Synergistic leaching of heavy metal-polycyclic aromatic hydrocarbon in co-contaminated soil by hydroxamate siderophore: Role of cation-π and chelation.

机构信息

College of Environment Science and Resources, Xiangtan University, Xiangtan 411105, PR China; Hunan Engineering Laboratory for High-Efficiency Purification Technology and its Application on Complex Heavy Metal Wastewater Treatment, Xiangtan 411105, PR China; Scientific Research Innovation Platform of Environmental Behavior and Control Principle about Novel Pollutants in Hunan Provincial Universities, Xiangtan 411105, PR China.

College of Environment Science and Resources, Xiangtan University, Xiangtan 411105, PR China; Hunan Engineering Laboratory for High-Efficiency Purification Technology and its Application on Complex Heavy Metal Wastewater Treatment, Xiangtan 411105, PR China; Scientific Research Innovation Platform of Environmental Behavior and Control Principle about Novel Pollutants in Hunan Provincial Universities, Xiangtan 411105, PR China.

出版信息

J Hazard Mater. 2022 Feb 15;424(Pt B):127514. doi: 10.1016/j.jhazmat.2021.127514. Epub 2021 Oct 15.

Abstract

Exploring a novel green efficient bioeluant is a golden key to unlock the ex-situ scale remediation of soil contaminated with heavy metals (HMs) and polycyclic aromatic hydrocarbons (PAHs). Hydroxamate siderophore (HDS) produced by Pseudomonas fluorescens HMP01, with certain hydrophobicity and strong coordination because of its special chemical structure (e.g., hydroxamic acid and dihydroxy quinoline chromophore), was used to investigate the bioleaching efficiency of HMs and PAHs from actual contaminated soils and underlying mechanisms. Results showed that leaching efficiency for HMs and PAHs from the co-contaminated soil was higher than that of single contaminated soil due to the cation-π interaction and coordination, which was closely related to the spacial configuration changes of the complex. HDS not only increased the bioleaching efficiency of cationic HMs by chelation (the leaching amount of Cd, Pb, Hg, Cu, Zn, and Ni achieved 27.5, 110.4, 6.9, 477.7, 10,606.9, and 137.4 mg/kg HDS, respectively) but also enhanced the bioleaching amount of PAHs by solubilization (the leaching amount of phenanthrene reached 90.2 mg/kg HDS. Also, the residual HDS in soils caused no significant ecological risk. As expected, HDS is a desirable bioeluant to promote the scale application of the ex-situ remediation of soil contaminated with HMs and PAHs.

摘要

探索新型绿色高效生物淋洗剂是解锁原位大规模修复重金属 (HM) 和多环芳烃 (PAH) 污染土壤的关键。荧光假单胞菌 HMP01 产生的羟肟酸类铁载体 (HDS) 具有一定的疏水性和强配位性,因为其特殊的化学结构(如羟肟酸和二羟基喹啉生色团),被用于研究从实际污染土壤中生物浸提 HM 和 PAH 的效率及其潜在机制。结果表明,由于阳离子-π 相互作用和配位作用,共污染土壤中 HM 和 PAH 的浸出效率高于单一污染土壤,这与配合物的空间构象变化密切相关。HDS 不仅通过螯合作用增加了阳离子 HM 的生物浸出效率(Cd、Pb、Hg、Cu、Zn 和 Ni 的浸出量分别达到 27.5、110.4、6.9、477.7、10606.9 和 137.4 mg/kg HDS),而且通过增溶作用增强了 PAH 的生物浸出量(菲的浸出量达到 90.2 mg/kg HDS)。此外,土壤中残留的 HDS 不会造成显著的生态风险。不出所料,HDS 是一种理想的生物淋洗剂,可以促进原位修复 HM 和 PAH 污染土壤的大规模应用。

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