Wang Jianxu, Xia Jicheng, Feng Xinbin
State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang, 550002, China.
State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang, 550002, China; University of Chinese Academy of Sciences, Beijing, 100049, China.
J Environ Manage. 2017 Jan 15;186(Pt 2):233-239. doi: 10.1016/j.jenvman.2016.05.031. Epub 2016 May 20.
Screening of optimal chelating ligands which not only have high capacities to enhance plant uptake of mercury (Hg) from soil but also can decrease bioavailable Hg concentration in soil is necessary to establish a viable chemically-assisted phytoextraction. Therefore, Brassica juncea was exposed to historically Hg-contaminated soil (total Hg, 90 mg kg) to investigate the efficiency of seven chelating agents [ammonium thiosulphate, sodium thiosulphate, ammonium sulfate, ammonium chloride, sodium nitrate, ethylenediaminetetraacetic acid (EDTA), and sodium sulfite] at enhancing Hg phytoextraction; the leaching of bioavailable Hg caused by these chelating agents was also investigated. The Hg concentration in control (treated with double-distilled water) plant tissues was below 1 mg kg. The remarkably higher Hg concentration was found in plants receiving ammonium thiosulphate and sodium sulfite treatments. The bioaccumulation factors and translocation factors of ammonium thiosulphate and sodium sulfite treatments were significantly higher than those of the other treatments. The more efficient uptake of Hg by plants upon treatment with ammonium thiosulphate and sodium sulfite compared to the other treatments might be explained by the formation of special Hg-thiosulphate complexes that could be preferentially taken up by the roots and transported in plant tissues. The application of sulfite significantly increased bioavailable Hg concentration in soil compared with that in initial soil and control soil, whereas ammonium thiosulphate significantly decreased bioavailable Hg concentration. The apparent decrease of bioavailable Hg in ammonium thiosulphate-treated soil compared with that in sodium sulfite-treated soil might be attributable to the unstable Hg-thiosulphate complexes formed between thiosulphate and Hg; they could react to produce less bioavailable Hg in the soil. The results of this study indicate that ammonium thiosulphate may be an optimal chelating ligand for phytoextraction due to its great potential to enhance Hg accumulation in plants while decreasing bioavailable Hg concentration in the soil.
筛选不仅具有高能力增强植物从土壤中吸收汞(Hg),而且能降低土壤中生物可利用汞浓度的最佳螯合配体,对于建立可行的化学辅助植物提取方法是必要的。因此,将芥菜暴露于历史汞污染土壤(总汞,90毫克/千克)中,以研究七种螯合剂[硫代硫酸铵、硫代硫酸钠、硫酸铵、氯化铵、硝酸钠、乙二胺四乙酸(EDTA)和亚硫酸钠]增强汞植物提取的效率;还研究了这些螯合剂引起的生物可利用汞的淋溶情况。对照(用双蒸水处理)植物组织中的汞浓度低于1毫克/千克。在接受硫代硫酸铵和亚硫酸钠处理的植物中发现汞浓度显著更高。硫代硫酸铵和亚硫酸钠处理的生物积累因子和转运因子显著高于其他处理。与其他处理相比,用硫代硫酸铵和亚硫酸钠处理后植物对汞的吸收更有效,这可能是由于形成了特殊的汞 - 硫代硫酸盐络合物,这些络合物可被根部优先吸收并在植物组织中运输。与初始土壤和对照土壤相比,亚硫酸盐的施用显著增加了土壤中生物可利用汞的浓度,而硫代硫酸铵显著降低了生物可利用汞的浓度。与亚硫酸钠处理的土壤相比,硫代硫酸铵处理的土壤中生物可利用汞的明显降低可能归因于硫代硫酸盐与汞之间形成的不稳定汞 - 硫代硫酸盐络合物;它们在土壤中反应生成生物可利用性较低的汞。本研究结果表明,硫代硫酸铵可能是植物提取的最佳螯合配体,因为它在增强植物中汞积累同时降低土壤中生物可利用汞浓度方面具有巨大潜力。