College of Resources and Environment, Yangtze University, Wuhan, China.
University of Leicester, University Road, LE1 7RH, Leicester, United Kingdom.
Bull Environ Contam Toxicol. 2022 May;108(5):909-916. doi: 10.1007/s00128-022-03473-y. Epub 2022 Mar 2.
Previous studies have reported that co-contamination can result in more complex effects on the phytoremediation efficiency of plants relative to those of a single pollutant. However, the effect of co-contamination on plant rhizosphere characteristics has rarely been revealed. This study was carried out to assess the changes in soil pH, the content and fractionation of dissolved organic matter (DOM), and the metal solubility in the rhizosphere of Arabidopsis thaliana when treated with Cd and Pb simultaneously. The results showed that co-contamination increased the concentrations of DOM by 24.8% and 30.9% in the rhizosphere soil of A. thaliana relative to individual Cd or Pb pollution, respectively. At the end of the experiment, co-contamination significantly decreased the initial soil pH from 6.6 ± 0.3 to 5.5 ± 0.4, whereas a decrease was not observed under Pb pollution alone. Variations in soil pH and DOM can change the fractions of the two metals in the rhizosphere soil of A. thaliana. DOM in co-contaminated soil showed a higher Cd (1.05 mg L) and Pb (0.75 mg L) extraction ability relative to that in the Cd-polluted (0.89 mg Cd L and 0.59 mg Pb L) or Pb-polluted (0.68 mg Cd L and 0.63 mg Pb L) soils. The soluble Cd content in the co-contaminated (0.44 mg L) soil was significantly lower than that in the Cd-polluted (0.71 mg L) soil because A. thaliana is a Cd accumulator, whereas the soluble Pb content showed the opposite trend (47.0 mg L vs. 37.4 mg L) because the species is a Pb excluder. Therefore, A. thaliana in co-contaminated soil would pose a leaching risk for the non-hyperaccumulated metals, thereby increasing the potential ecological risk during the phytoremediation process.
先前的研究报告指出,与单一污染物相比,共污染可能会对植物的植物修复效率产生更复杂的影响。然而,共污染对植物根际特征的影响很少被揭示。本研究旨在评估 Cd 和 Pb 同时处理拟南芥时,根际土壤 pH 值、溶解有机质(DOM)含量和形态以及金属可溶性的变化。结果表明,与单独的 Cd 或 Pb 污染相比,共污染分别使拟南芥根际土壤 DOM 浓度增加了 24.8%和 30.9%。实验结束时,共污染使初始土壤 pH 值从 6.6±0.3 显著降低至 5.5±0.4,而单独 Pb 污染则没有观察到这种降低。土壤 pH 值和 DOM 的变化可以改变两种金属在拟南芥根际土壤中的形态。共污染土壤中的 DOM 对 Cd(1.05mg L)和 Pb(0.75mg L)的提取能力高于 Cd 污染土壤(0.89mg Cd L 和 0.59mg Pb L)或 Pb 污染土壤(0.68mg Cd L 和 0.63mg Pb L)。共污染土壤中的可溶性 Cd 含量(0.44mg L)明显低于 Cd 污染土壤(0.71mg L),因为拟南芥是 Cd 积累物,而可溶性 Pb 含量则表现出相反的趋势(47.0mg L 对 37.4mg L),因为该物种是 Pb 排斥物。因此,共污染土壤中的拟南芥可能对非超积累金属具有浸出风险,从而增加植物修复过程中的潜在生态风险。