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Effects of plant arsenic uptake and heavy metals on arsenic distribution in an arsenic-contaminated soil

机译:植物吸收砷和重金属对砷污染土壤中砷分布的影响

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This study examined the effects of heavy metals and plant arsenic uptake on soil arsenic distribution. Chemical fractionation of an arsenic-contaminated soil spiked with 50 or 200 mg kg~(-1) Ni, Zn, Cd or Pb was performed before and after growing the arsenic hyperaccumulator Pteris vittata L for 8 weeks using NH_4Cl (water-soluble plus exchangeable, WE-As), NH_4F (Al-As), NaOH (Fe-As), and H_2SO_4 (Ca-As). Arsenic in the soil was present primarily as the recalcitrant forms with Ca-As being the dominant fraction (45%). Arsenic taken up by P. vittata was from all fractions though Ca-As contributed the most (51—71% reduction). After 8 weeks of plant growth, the Al-As and Fe-As fractions were significantly (p < 0.01) greater in the metal-spiked soils than the control, with changes in the WE-As fraction being significantly (p = 0.007) correlated with plant arsenic removal. The plant's ability to solubilize soil arsenic from recalcitrant fractions may have enhanced its ability to hyperaccumulate arsenic.
机译:这项研究检查了重金属和植物吸收砷对土壤砷分布的影响。使用NH_4Cl(水溶性加可交换的)在砷超富集菌Pteris vittata L生长8周之前和之后,对掺有50或200 mg kg〜(-1)Ni,Zn,Cd或Pb的砷污染土壤进行化学分馏。 ,WE-As),NH_4F(Al-As),NaOH(Fe-As)和H_2SO_4(Ca-As)。土壤中的砷主要以顽固形式存在,其中Ca-As是主要成分(45%)。尽管Ca-As贡献最大(减少了51-71%),但P. vittata吸收的砷来自所有馏分。在植物生长8周后,金属掺入土壤中的Al-As和Fe-As含量显着(p <0.01)高于对照,而WE-As含量的变化具有明显的相关性(p = 0.007)去除植物中的砷。植物从顽固级分中溶解土壤砷的能力可能增强了其过分积累砷的能力。

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