4.7 Article

Effects of arbuscular mycorrhizal fungi on the growth and toxic element uptake of Phragmites australis (Cav.) Trin. ex Steud under zinc/cadmium stress

期刊

出版社

ACADEMIC PRESS INC ELSEVIER SCIENCE
DOI: 10.1016/j.ecoenv.2021.112023

关键词

Rhizophagus irregularis; Phytoremediation; Zn-Cd composite stress; Concentration dependence; Interaction effect

资金

  1. National Natural Science Foundation of China (China) [51978199, 31570505]
  2. Heilongjiang Province Applied Technology Research and Development Program (China) [GA20C014]
  3. College of Life Sciences, Heilongjiang University [R717169]

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The study shows that AMF can alleviate the toxic effects of Zn and Cd on Phragmites australis through different regulatory patterns, including increasing plant biomass and regulating mechanisms under different concentrations of toxic elements. Enzyme activities such as SOD and APX increase under Zn stress, while multiple enzymes show significant increases under high concentrations of Cd.
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 (TFZn) was concentration-dependent. AMF increased the TFZn 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 TFCd decreased. AMF were also found to change the interaction of ZnxCd. In the absence of AMF, Cd exposure decreased the Zn concentrations in P. australis at Zn-100 mg/L and Zn-300 mg/L, while it increased the contents of Zn at Zn-700 mg/L. 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.

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