State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing, 210023, PR China.
State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing, 210023, PR China.
Environ Pollut. 2019 May;248:667-675. doi: 10.1016/j.envpol.2019.02.047. Epub 2019 Feb 26.
Photodegradation is an important pathway for monomethylmercury (MeHg) degradation in aquatic ecosystems. In this process, dissolved organic matter (DOM) plays an essential role. However, little information is available regarding the photo-transformation of MeHg in shallow aquatic environments, where a significant portion of MeHg is associated with soil suspensions. In this study, 14 soils sampled from different sites in China were used to simulate these conditions. Our results clearly demonstrated that soil organic matter (SOM) was the most important factor controlling the MeHg photodegradation in suspension. Degradation in this heterogeneous aqueous system was shown to be mediated by the O produced by organic matter on the surface of the soil particles rather than by DOM. This was confirmed by the strong correlation between the kinetics rate constant of MeHg degradation and steady state concentrations of O (R = 0.81). Our results propose a new pathway of MeHg induced by sediment soils under sunlight irradiation. Identification of this pathway may improve the estimates of potential ecological risk of Hg in shallow field ecosystems.
光降解是水生生态系统中单甲基汞(MeHg)降解的重要途径。在这个过程中,溶解有机质(DOM)起着至关重要的作用。然而,关于浅水生态环境中 MeHg 的光转化的信息却很少,在这些环境中,很大一部分 MeHg 与土壤悬浮体有关。在这项研究中,我们使用了从中国不同地点采集的 14 种土壤来模拟这些条件。我们的研究结果清楚地表明,土壤有机质(SOM)是控制悬浮体中 MeHg 光降解的最重要因素。在这个非均相水体系中,降解是由土壤颗粒表面有机质产生的 O 介导的,而不是由 DOM 介导的。MeHg 降解动力学速率常数与 O 的稳态浓度之间存在很强的相关性(R = 0.81),这证实了这一点。我们的研究结果提出了一种在阳光照射下由沉积物土壤引发的 MeHg 新的降解途径。识别这种途径可能会提高对浅层田间生态系统中汞潜在生态风险的估计。