College of Landscape Architecture, Nanjing Forestry University, Nanjing, People's Republic of China.
Environ Technol. 2024 Jan;45(3):532-543. doi: 10.1080/09593330.2022.2114858. Epub 2022 Aug 29.
A pot experiment was conducted to explore the effects of copper (Cu) tailings with various proportions in the substrate on seed germination and morphological traits of the plant. Concurrently, to identify the adaptive and tolerance strategies of the plant to Cu tailings, the uptake and accumulation of the plant to heavy metals, variations in soil enzymatic activities, and metal speciation in the blank, rhizospheric, and non-rhizospheric soils were estimated. Cu tailings at 25% proportion in the substrate exerted no significant negative effects on seed germination and seedling growth. However, Cu tailings at higher proportions (≧50%) inhibited seed germination and disturbed the plant physiological metabolism and growth. More biomass allocated to the plant roots could contribute to more heavy metals being immobilized, arresting their translocation from roots to shoots. This was accepted as a crucial defense mechanism for the plant against heavy metal co-contamination. The plant can improve the biological properties of Cu tailings in terms of enhanced invertase and phosphatase activities. And in turn, this can effectively alleviate heavy metal phytotoxicity. Simultaneously, it markedly decreased exchangeable Cu and Zn content in the rhizosphere in 25% Cu tailings treatments. In 50% Cu tailings treatment, no differences were observed in Zn speciation between rhizosphere and non-rhizosphere soils. In 75% Cu tailings, compared to the non-rhizosphere, an obvious reduction in exchangeable Cu in rhizosphere occurred, while an opposite tendency was demonstrated in carbonate-bound Zn. The plant could successfully colonize in Cu tailings, and represent a phytoremediation potential in Cu tailings.
采用盆栽试验研究了不同比例铜尾矿添加到基质中对植物种子萌发和形态特征的影响。同时,为了鉴定植物对铜尾矿的适应和耐受策略,评估了植物对重金属的吸收和积累、土壤酶活性的变化以及空白、根际和非根际土壤中金属的形态。在基质中添加 25%比例的铜尾矿对种子萌发和幼苗生长没有显著的负面影响。然而,添加更高比例(≥50%)的铜尾矿会抑制种子萌发并扰乱植物的生理代谢和生长。更多的生物量分配到植物根部有助于固定更多的重金属,阻止它们从根部向地上部转移。这被认为是植物抵御重金属复合污染的一个重要防御机制。植物可以通过提高转化酶和磷酸酶的活性来改善铜尾矿的生物学特性。反过来,这可以有效地减轻重金属的植物毒性。同时,在 25%铜尾矿处理中,根际可交换态 Cu 和 Zn 含量明显降低。在 50%铜尾矿处理中,根际和非根际土壤中 Zn 的形态没有差异。在 75%铜尾矿中,与非根际相比,根际中可交换态 Cu 明显减少,而碳酸盐结合态 Zn 的趋势则相反。该植物能够成功地在铜尾矿中定植,表现出在铜尾矿中进行植物修复的潜力。