co-pollutants from the environment. The effects of pH and exchange capacity
(EC) in contaminated systems that govern transformations of HMs in both lowland
and upland rice paddy fields need analysis.
Solution-phase and solid-phase speciation of HMs in water and soil using
advanced techniques must be further studied. Further research is required to identify
biochemical mechanisms involved in the different HM uptake in plants, because
little research has been conducted on the rhizosphere processes underpinning effective phytoextraction technology for HM cleanup from contaminated soils.
Employing different beneficial microbial communities such as PGPR and mycorrhizal organisms enhances the remediation process effectively. Thus, selection and
identification of new microbial strains with these qualities are required to better
understand their functions and interactions in the rhizosphere, that is, the plant roots,
among metals, microbes, and soil systems. Further analysis of the HM-enriched
plant biomass is needed for reclamation or safe decontamination. Practical
approaches are needed for successful application of the various remediation technologies, such as hyper-accumulators, chelators, microbes, and soil amendments
suitable for effective remediation of different HM-polluted environmental sites.
Acknowledgments The authors are grateful for financial support from a Research Fund for
International Young Scientists from National Natural Science Foundation of China (Grant
No. 31750110469), and The Introduction of talent research start-up found (No. Z101021803).
We also thank our laboratory colleagues and research staff members for their constructive advice
and help.
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