College of Environmental Science and Engineering, Hunan University, Changsha 410082, China; Key Laboratory of Environmental Biology and Pollution Control (Hunan University), Ministry of Education, Changsha 410082, China.
College of Environmental Science and Engineering, Hunan University, Changsha 410082, China; Key Laboratory of Environmental Biology and Pollution Control (Hunan University), Ministry of Education, Changsha 410082, China.
J Hazard Mater. 2023 Sep 5;457:131682. doi: 10.1016/j.jhazmat.2023.131682. Epub 2023 May 22.
The mechanisms by which eutrophication affects methylmercury (MeHg) production have not been comprehensively summarized, which hinders accurately predicting the MeHg risk in eutrophic lakes. In this review, we first discussed the effects of eutrophication on biogeochemical cycle of mercury (Hg). Special attentions were paid to the roles of algal organic matter (AOM) and iron (Fe)-sulfur (S)-phosphorus (P) dynamics in MeHg production. Finally, the suggestions for risk control of MeHg in eutrophic lakes were proposed. AOM can affect in situ Hg methylation by stimulating the abundance and activities of Hg methylating microorganisms and regulating Hg bioavailability, which are dependent on bacteria-strain and algae species, the molecular weight and composition of AOM as well as environmental conditions (e.g., light). Fe-S-P dynamics under eutrophication including sulfate reduction, FeS formation and P release could also play crucial but complicated roles in MeHg production, in which AOM may participate through influencing the dissolution and aggregation processes, structural order and surface properties of HgS nanoparticles (HgS). Future studies should pay more attention to the dynamics of AOM in responses to the changing environmental conditions (e.g., light penetration and redox fluctuations) and how such variations will subsequently affect MeHg production. The effects of Fe-S-P dynamics on MeHg production under eutrophication also deserve further investigations, especially the interactions between AOM and HgS. Remediation strategies with lower disturbance, greater stability and less cost like the technology of interfacial O nanobubbles are urgent to be explored. This review will deepen our understanding of the mechanisms of MeHg production in eutrophic lakes and provide theoretical guidance for its risk control.
富营养化影响甲基汞(MeHg)生成的机制尚未得到全面总结,这阻碍了对富营养化湖泊中 MeHg 风险的准确预测。在本综述中,我们首先讨论了富营养化对汞(Hg)生物地球化学循环的影响。特别关注了藻类有机质(AOM)和铁(Fe)-硫(S)-磷(P)动态在 MeHg 生成中的作用。最后,提出了富营养化湖泊中 MeHg 风险控制的建议。AOM 可以通过刺激 Hg 甲基化微生物的丰度和活性以及调节 Hg 的生物利用度来影响原位 Hg 甲基化,这取决于细菌菌株和藻类种类、AOM 的分子量和组成以及环境条件(如光照)。富营养化下的 Fe-S-P 动态,包括硫酸盐还原、FeS 形成和 P 释放,也可以在 MeHg 生成中发挥关键但复杂的作用,其中 AOM 可能通过影响 HgS 纳米颗粒(HgS)的溶解和聚集过程、结构有序性和表面特性来参与其中。未来的研究应更多地关注 AOM 对环境条件变化(如透光率和氧化还原波动)的动态响应,以及这种变化将如何随后影响 MeHg 的生成。富营养化条件下 Fe-S-P 动态对 MeHg 生成的影响也值得进一步研究,特别是 AOM 和 HgS 之间的相互作用。修复策略具有较低的干扰、更大的稳定性和更低的成本,如界面 O 纳米气泡技术,迫切需要探索。本综述将加深我们对富营养化湖泊中 MeHg 生成机制的理解,并为其风险控制提供理论指导。