State Key Lab of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, No. 73, Huanghe Road, Nangang District, Harbin 150090, People's Republic of China.
State Key Lab of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, No. 73, Huanghe Road, Nangang District, Harbin 150090, People's Republic of China.
Ecotoxicol Environ Saf. 2021 Apr 15;213:112023. doi: 10.1016/j.ecoenv.2021.112023. Epub 2021 Feb 9.
Arbuscular mycorrhizal fungi (AMF) play an important role in improving plant tolerance and accumulation of zinc (Zn) and cadmium (Cd). The growth, physiology and absorption of elements and transport in Phragmites australis (P. australis) were investigated under Zn and Cd stress to identify the transport mechanisms of toxic trace elements (TE) under the influence of AMF. Thus, AMF were observed to alleviate the toxic effects of Zn and Cd on P. australis by increasing plant biomass and through different regulatory patterns under different TE concentrations. The activities of superoxide dismutase (SOD) and ascorbate peroxidase (APX) increased under Zn stress, and the activities of SOD, catalase (CAT), peroxidase (POD), and APX significantly increased under high concentrations of Cd. AMF differ in their strategies of regulating the transport of different metals under TE stress. Under Zn stress, the concentration of Zn in P. australis decreased by 10-57%, and the effect on Zn translocation factor (TF) was concentration-dependent. AMF increased the TF under low concentration stress, but decreased under high concentration stress. Under Cd stress, the concentration of Cd increased by as much as 17-40%, and the TF decreased. AMF were also found to change the interaction of Zn×Cd. In the absence of AMF, Cd exposure decreased the Zn concentrations in P. australis at Zn and Zn, while it increased the contents of Zn at Zn. The opposite trend was observed following treatment with AMF. However, regardless of the concentration of Cd, the addition of Zn decreased the concentration of Cd in both treatments in both the presence and absence of AMF. Under different TE stress conditions, the regulation of metal elements by AMF in host plants does not follow a single strategy but a trade-off between different trends of transportations. The findings of our study are important for applying AMF-P. australis systems in the phytoremediation of Zn-Cd co-contaminated ecosystems.
丛枝菌根真菌(AMF)在提高植物对锌(Zn)和镉(Cd)的耐受性和积累能力方面发挥着重要作用。本研究在 Zn 和 Cd 胁迫下,调查了芦苇(P. australis)的生长、生理和元素吸收以及运输,以确定 AMF 影响下有毒痕量元素(TE)的运输机制。结果表明,AMF 通过增加植物生物量和在不同 TE 浓度下通过不同的调节模式来减轻 Zn 和 Cd 对 P. australis 的毒性影响。在 Zn 胁迫下,超氧化物歧化酶(SOD)和抗坏血酸过氧化物酶(APX)的活性增加,而在高浓度 Cd 下,SOD、过氧化氢酶(CAT)、过氧化物酶(POD)和 APX 的活性显著增加。AMF 在 TE 胁迫下对不同金属的运输调节策略存在差异。在 Zn 胁迫下,P. australis 中 Zn 的浓度降低了 10-57%,对 Zn 转运因子(TF)的影响呈浓度依赖性。AMF 在低浓度胁迫下增加了 TF,但在高浓度胁迫下降低了 TF。在 Cd 胁迫下,Cd 的浓度增加了 17-40%,而 TF 降低了。AMF 还改变了 Zn×Cd 的相互作用。在没有 AMF 的情况下,Cd 暴露降低了 Zn 和 Zn 处理下 P. australis 中 Zn 的浓度,而增加了 Zn 处理下 P. australis 中 Zn 的含量。在用 AMF 处理后观察到相反的趋势。然而,无论 Cd 的浓度如何,在有和没有 AMF 的情况下,添加 Zn 都会降低两种处理中 Cd 的浓度。在不同的 TE 胁迫条件下,AMF 在宿主植物中对金属元素的调节并不遵循单一策略,而是在不同运输趋势之间的权衡。本研究结果对于应用 AMF-P. australis 系统在 Zn-Cd 复合污染生态系统的植物修复中具有重要意义。