Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Institute of Soil and Water Resources and Environmental Science, College of Environmental and Resource Sciences, Zhejiang University, Hangzhou 310058, China.
School of Ecology and Environment, Anhui Normal University, Wuhu, Anhui 241002, China.
Environ Sci Technol. 2022 Oct 4;56(19):14146-14153. doi: 10.1021/acs.est.2c03147. Epub 2022 Sep 19.
Selenate enhances arsenic (As) accumulation in As-hyperaccumulator , but the associated molecular mechanisms are unclear. Here, we investigated the mechanisms of selenate-induced arsenic accumulation by exposing to 50 μM arsenate (AsV) and 1.25 (Se) or 5 μM (Se) selenate in hydroponics. After 2 weeks, plant biomass, plant As and Se contents, As speciation in plant and growth media, and important genes related to As detoxification in were determined. These genes included P transporters and (AsV uptake), arsenate reductases and (AsV reduction), and arsenite (AsIII) antiporters and (AsIII translocation) in the roots, and AsIII antiporters and (AsIII sequestration) in the fronds. The results show that Se was more effective than Se in increasing As accumulation in both roots and fronds, which increased by 27 and 153% to 353 and 506 mg kg. The As speciation analyses show that selenate increased the AsIII levels in , with 124-282% more AsIII being translocated into the fronds. The qPCR analyses indicate that Se upregulated the gene expression of by 1.2-fold, and and by 1.0- to 2.5-fold in the roots, and and by 0.6- to 1.1-fold in the fronds under AsV treatment. Though arsenate enhanced gene expression of P transporters and , selenate had little effect. Our results indicate that selenate effectively increased As accumulation in , mostly by increasing reduction of AsV to AsIII in the roots, AsIII translocation from the roots to fronds, and AsIII sequestration into the vacuoles in the fronds. The results suggest that selenate may be used to enhance phytoremediation of As-contaminated soils using .
亚硒酸盐增强砷(As)在砷超富集植物中的积累,但相关的分子机制尚不清楚。在这里,我们通过水培暴露于 50 μM 砷酸盐(AsV)和 1.25(Se)或 5 μM(Se)亚硒酸盐来研究亚硒酸盐诱导砷积累的机制。2 周后,测定了植物生物量、植物 As 和 Se 含量、植物和生长介质中的 As 形态以及 中与 As 解毒相关的重要基因。这些基因包括 P 转运体 和 (AsV 摄取)、砷酸盐还原酶 和 (AsV 还原)以及砷酸盐(AsIII)反转运体 和 (AsIII 转运)在根中,和 AsIII 反转运体 和 (AsIII 螯合)在叶子中。结果表明,Se 比 Se 更有效地增加了 和 的根和叶中的 As 积累,分别增加了 27%和 153%,达到 353 和 506mg/kg。As 形态分析表明,亚硒酸盐增加了 的 AsIII 水平,有 124-282%更多的 AsIII 被转运到叶子中。qPCR 分析表明,Se 使根中 基因的表达上调了 1.2 倍,而 和 基因的表达上调了 1.0-2.5 倍,而 和 基因的表达上调了 0.6-1.1 倍。尽管砷酸盐增强了 P 转运体 和 的基因表达,但亚硒酸盐的影响很小。我们的结果表明,亚硒酸盐有效地增加了 的 As 积累,主要是通过增加根中 AsV 向 AsIII 的还原、AsIII 从根向叶的转运以及叶中的 AsIII 螯合到液泡中。这些结果表明,亚硒酸盐可能用于增强利用 对含砷土壤的植物修复。