弱分层饮用水水库中锰的地球化学和水文控制因素

Yi Sang, Olivia Pietz, Emily Christiansen, Lena Abu-Ali, Christopher J. Pollock, Christopher W. Sinton, Roxanna Johnston, Matthew C. Reid
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摘要

水库分层会导致水处理设施原水取水口的溶解锰(Mn)浓度过高,使处理过程复杂化。锰在分层湖泊中的释放和沉淀途径尚不完全清楚。我们在 2021 年和 2022 年对纽约州一个瞬时分层水库中的锰和其他水质参数进行了监测。2022 年的中度干旱增加了分层的持续时间,导致原水取水口的锰浓度高达 35 μM。锰-钙(Ca)混合碳酸盐(而非菱锰矿(MnCO3))在表层水过饱和,利用 X 射线吸收光谱在悬浮颗粒中发现了(Ca,Mn)CO3 矿物。然而,尚不清楚含锰碳酸盐是在水体中沉淀还是从湖底沉积物中悬浮出来的,根据 EXAFS 分析,湖底沉积物中有 31% 的(Ca,Mn)CO3。湖底沉积物中锰(II)的普遍存在表明,沉积锰(III/IV)氧化物的还原溶解并不是锰释放到分层水体中的唯一触发因素,pH值驱动效应也可能影响锰的释放。在气候变化的影响下,气温升高、天气干燥,预计将加剧湖泊和水库的分层现象,从而可能加剧地表饮用水源中锰浓度过高的问题。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Geochemical and Hydrological Controls on Manganese in a Weakly-Stratified Drinking Water Reservoir

Geochemical and Hydrological Controls on Manganese in a Weakly-Stratified Drinking Water Reservoir
Reservoir stratification can lead to high concentrations of dissolved manganese (Mn) in the raw water intake of water treatment facilities, complicating treatment processes. Pathways for Mn release to and precipitation in stratified lakes are not fully understood. We monitored Mn and other water quality parameters in a transiently stratified reservoir in New York State in 2021 and 2022. Moderate drought conditions in 2022 increased the duration of stratification, leading to Mn concentrations up to 35 μM in the raw water intake. Mixed Mn-calcium (Ca) carbonates, but not rhodochrosite (MnCO3), were supersaturated in the epilimnion, and (Ca,Mn)CO3 minerals were identified in suspended particulates using X-ray absorption spectroscopy. However, it was unclear whether Mn-bearing carbonates precipitated in the water column or were suspended from lake-bottom sediments, which consisted of 31% (Ca,Mn)CO3 based on EXAFS analysis. The prevalence of Mn(II) in lake-bottom sediments suggests that reductive dissolution of sedimentary Mn(III/IV) oxides is not the only trigger for Mn release into stratified water columns and that pH-driven effects may also influence Mn release. Warmer temperatures and drier weather under climate change are expected to increase stratification in lakes and reservoirs, likely exacerbating problems associated with high Mn concentrations in surface drinking water sources.
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