Duke University, Department of Civil & Environmental Engineering, 121 Hudson Hall, Durham, North Carolina 27708, USA.
Iowa State University, Department of Civil, Construction, and Environmental Engineering, Ames, Iowa 50011, USA.
Environ Sci Process Impacts. 2016 Nov 9;18(11):1427-1439. doi: 10.1039/c6em00458j.
Mercury (Hg) associated with coal ash is an environmental concern, particularly if the release of coal ash to the environment is associated with the conversion of inorganic Hg to methylmercury (MeHg), a bioaccumulative form of Hg that is produced by anaerobic microorganisms. In this study, sediment slurry microcosm experiments were performed to understand how spilled coal ash might influence MeHg production in anaerobic sediments of an aquatic ecosystem. Two coal ash types were used: (1) a weathered coal ash; and (2) a freshly collected, unweathered fly ash that was relatively enriched in sulfate and Hg compared to the weathered ash. These ash samples were added to anaerobic sediment slurries constructed with a relatively pristine sediment (containing 0.03 mg kg Hg) and a Hg-contaminated sediment (containing 0.29 mg kg Hg). The results of these experiments showed negligible net production of MeHg in microcosms with no ash and in microcosms amended with the low sulfate/low Hg ash. In contrast, slurry microcosms amended with high sulfate/high Hg ash showed increases in total MeHg content that was 2 to 3 times greater than control microcosms without ash (p < 0.001). 16S amplicon sequencing of microbial communities in the slurries indicated that the coal ash addition generally increased the relative abundance of the methylating microbial community, including sulfate-reducing bacteria and iron-reducing bacteria species that are known to be efficient methylators of Hg. The stimulation of these microorganisms was likely caused by the release of substrates (sulfate and Fe) originating from the ash. Overall, the results highlight the need to incorporate both environmental parameters and coal ash characteristics into risk assessments that guide coal ash management and disposal.
汞(Hg)与煤灰有关,是一个环境问题,特别是如果煤灰释放到环境中,会导致无机汞转化为甲基汞(MeHg),后者是一种生物累积形式的汞,由厌氧微生物产生。在这项研究中,进行了沉积物泥浆微宇宙实验,以了解溢出的煤灰如何影响水生生态系统中厌氧沉积物中 MeHg 的产生。使用了两种类型的煤灰:(1)风化煤灰;(2)刚收集的、未风化的飞灰,与风化灰相比,它相对富含硫酸盐和 Hg。将这些灰分样品添加到用相对原始沉积物(含 0.03 mg kg Hg)和 Hg 污染沉积物(含 0.29 mg kg Hg)构建的厌氧沉积物泥浆微宇宙中。这些实验的结果表明,在没有煤灰的微宇宙中和在添加低硫酸盐/低 Hg 煤灰的微宇宙中,MeHg 的净产生可忽略不计。相比之下,添加高硫酸盐/高 Hg 煤灰的泥浆微宇宙中总 MeHg 含量增加了 2 到 3 倍,明显高于没有煤灰的对照微宇宙(p < 0.001)。泥浆中微生物群落的 16S 扩增子测序表明,煤灰的添加通常会增加甲基化微生物群落的相对丰度,包括硫酸盐还原菌和铁还原菌,它们是已知的高效 Hg 甲基化菌。这些微生物的刺激可能是由来自煤灰的基质(硫酸盐和 Fe)的释放引起的。总的来说,研究结果强调需要将环境参数和煤灰特性纳入风险评估中,以指导煤灰的管理和处置。