Department of Physical and Environmental Sciences, University of Toronto Scarborough, Ontario, Canada.
Department of Biology, Lakehead University, Thunder Bay, Ontario, Canada.
Environ Sci Process Impacts. 2022 Jun 22;24(6):932-944. doi: 10.1039/d2em00064d.
Sulphate and dissolved organic matter (DOM) in freshwater systems may regulate the formation of methylmercury (MeHg), a potent neurotoxin that biomagnifies in aquatic ecosystems. While many boreal lakes continue to recover from decades of elevated atmospheric sulphate deposition, little research has examined whether historically high sulphate concentrations can result in persistently elevated MeHg production and accumulation in aquatic systems. This study used sediment from a historically sulphate-impacted lake and an adjacent reference lake in northwestern Ontario, Canada to investigate the legacy effects of sulphate pollution, as well as the effects of newly added sulphate, natural organic matter (NOM) of varying sulphur content and a sulphate reducing bacteria (SRB) inhibitor on enhancing or inhibiting the Hg methylation and demethylation activity ( and ) in the sediment. We found that and MeHg concentrations in sulphate-impacted lake sediment were significantly greater than in reference lake sediment. Further adding sulphate or NOM with different sulphur content to sediment of both lakes did not significantly change . The addition of a SRB inhibitor resulted in lower only in sulphate-impacted sediment, but methylation was not entirely depressed. Methylmercury demethylation potentials in sediment were consistent across lakes and experimental treatments, except for some impacts related to SRB inhibitor additions in the reference lake sediment. Overall, a broader community of microbes beyond SRB may be methylating Hg and demethylating MeHg in this system. This study reveals that legacies of sulphate pollution in boreal lakes may persist for decades in stimulating elevated Hg methylation in sediment.
淡水系统中的硫酸盐和溶解有机物质(DOM)可能会影响甲基汞(MeHg)的形成,甲基汞是一种在水生生态系统中具有生物放大作用的强效神经毒素。尽管许多北方湖泊已经从几十年的大气硫酸盐沉降中恢复过来,但很少有研究考察历史上高硫酸盐浓度是否会导致水生系统中持续升高的 MeHg 产量和积累。本研究使用来自加拿大安大略省西北部一个历史上受硫酸盐影响的湖泊和一个相邻参照湖泊的沉积物,调查硫酸盐污染的遗留效应,以及新添加的硫酸盐、具有不同硫含量的天然有机物质(NOM)和硫酸盐还原菌(SRB)抑制剂对增强或抑制沉积物中 Hg 甲基化和脱甲基活性( 和 )的影响。我们发现,受硫酸盐影响的湖泊沉积物中的 和 MeHg 浓度明显高于参照湖泊沉积物。进一步向两个湖泊的沉积物中添加硫酸盐或具有不同硫含量的 NOM 并没有显著改变 。在受硫酸盐影响的沉积物中,SRB 抑制剂的添加仅导致 降低,但甲基化并未完全受到抑制。除了参照湖泊沉积物中与 SRB 抑制剂添加有关的一些影响外,沉积物中的 MeHg 脱甲基潜力在湖泊和实验处理之间是一致的。总的来说,除了参照湖泊沉积物中与 SRB 抑制剂添加有关的一些影响外,除了硫酸盐还原菌之外,更广泛的微生物群落可能会在该系统中使 Hg 甲基化并使 MeHg 脱甲基。本研究表明,北方湖泊硫酸盐污染的遗留效应可能会持续数十年,刺激沉积物中 Hg 的甲基化。