Institut F.-A. Forel, University of Geneva, Route de Suisse 10, CH-1290 Versoix, Genève, Switzerland.
LCABIE-IPREM, UMR 5254 CNRS - Université de Pau et des Pays de l'Adour, Hélioparc, 64053 Pau, France.
Water Res. 2015 Sep 1;80:245-55. doi: 10.1016/j.watres.2015.04.039. Epub 2015 May 9.
Sewage treatment plants (STPs) are important point sources of mercury (Hg) to the environment. STPs are also significant sources of iron when hydrated ferric oxide (HFO) is used as a dephosphatation agent during water purification. In this study, we combined geochemical and microbiological characterization with Hg speciation and sediment amendments to evaluate the impact of STP's effluents on monomethylmercury (MMHg) production. The highest in-situ Hg methylation was found close to the discharge pipe in subsurface sediments enriched with Hg, organic matter, and iron. There, ferruginous conditions were prevailing with high concentrations of dissolved Fe(2+) and virtually no free sulfide in the porewater. Sediment incubations demonstrated that the high MMHg production close to the discharge was controlled by low demethylation yields. Inhibition of dissimilatory sulfate reduction with molybdate led to increased iron reduction rates and Hg-methylation, suggesting that sulfate-reducing bacteria (SRB) may not have been the main Hg methylators under these conditions. However, Hg methylation in sediments amended with amorphous Fe(III)-oxides was only slightly higher than control conditions. Thus, in addition to iron-reducing bacteria, other non-SRB most likely contributed to Hg methylation. Overall, this study highlights that sediments impacted by STP discharges can become local hot-spots for Hg methylation due to the combined inputs of i) Hg, ii) organic matter, which fuels bacterial activities and iii) iron, which keeps porewater sulfide concentration low and hence Hg bioavailable.
污水处理厂(STP)是环境中汞(Hg)的重要点源。当在水净化过程中使用水合氧化铁(HFO)作为除磷剂时,STP 也是铁的重要来源。在这项研究中,我们结合地球化学和微生物学特征、Hg 形态分析以及沉积物改良剂,评估 STP 废水对一甲基汞(MMHg)生成的影响。在富含 Hg、有机物和铁的地下沉积物中,我们发现靠近排放口的原位 Hg 甲基化程度最高。在那里,存在着高铁条件,溶解的 Fe(2+)浓度很高,而孔隙水中几乎没有游离的硫化物。沉积物孵育实验表明,靠近排放口的高 MMHg 生成受低脱甲基化产率控制。用钼酸盐抑制异化硫酸盐还原会导致铁还原速率和 Hg 甲基化增加,这表明在这些条件下,硫酸盐还原菌(SRB)可能不是主要的 Hg 甲基化菌。然而,在添加无定形 Fe(III)氧化物的沉积物中,Hg 甲基化作用仅略高于对照条件。因此,除了铁还原菌之外,其他非硫酸盐还原菌很可能也促成了 Hg 甲基化。总的来说,这项研究强调了受 STP 排放影响的沉积物由于以下三种因素的综合作用,可能成为 Hg 甲基化的局部热点:i)Hg,ii)为细菌活动提供燃料的有机物,以及 iii)保持孔隙水硫化物浓度低从而使 Hg 具有生物可利用性的铁。