Center for Environmental Nanoscience and Risk, Arnold School of Public Health, University of South Carolina, Columbia, SC, 29201, USA.
Faculté des Sciences, Institut Forel, Université de Genève, Uni Vogt, 66 Bd Carl Vogt, 1211, Genève, Switzerland.
Environ Sci Pollut Res Int. 2019 Feb;26(6):5251-5266. doi: 10.1007/s11356-018-1416-5. Epub 2018 Feb 10.
This study investigates the spatiotemporal variability of major and trace elements, dissolved organic carbon (DOC), total dissolved solids (TDS), and suspended particulate matter (SPM) in surface waters of several hydrosystems of the Loire River watershed in France. In particular, this study aims to delineate the impact of the abovementioned water physicochemical parameters on natural iron and manganese physical speciation (homoaggregation/heteroaggregation) among fine colloidal and dissolved (< 10 nm), colloidal (10-450 nm) and particulate (> 450 nm) phases in Loire River watershed. Results show that the chemistry of the Loire River watershed is controlled by two end members: magmatic and metamorphic petrographic context on the upper part of the watershed; and sedimentary rocks for the middle and low part of the Loire. The percentage of particulate Fe and Mn increased downstream concurrent with the increase in SPM and major cations concentration, whereas the percentage of colloidal Fe and Mn decreased downstream. Transmission electron microscopy analyses of the colloidal and particulate fractions (from the non-filtered water sample) revealed that heteroaggregation of Fe and Mn rich natural nanoparticles and natural organic matter to the particulate phase is the dominant mechanism. The heteroaggregation controls the partitioning of Fe and Mn in the different fractions, potentially due to the increase in the ionic strength, and divalent cations concentration downstream, and SPM concentration. These findings imply that SPM concentration plays an important role in controlling the fate and behavior of Fe and Mn in various sized fractions. Graphical abstract Physical speciation by heteroaggregation of (Fe-Mn) compounds: high [SPM] → [Fe-Mn] particulate faction; low {SPM] → [Fe-Mn] colloid-dissolved fraction.
本研究调查了法国卢瓦尔河流域几个水系统地表水中主要和微量元素、溶解有机碳 (DOC)、总溶解固体 (TDS) 和悬浮颗粒物 (SPM) 的时空变化。特别是,本研究旨在描绘上述水物理化学参数对天然铁和锰物理形态(同聚/异聚)的影响,这些形态存在于细小胶体和溶解(<10nm)、胶体(10-450nm)和颗粒(>450nm)相中。结果表明,卢瓦尔河流域的化学性质受两个端元控制:流域上游的火成岩和变质岩岩石学背景;以及卢瓦尔河中下游的沉积岩。颗粒态 Fe 和 Mn 的百分比随着 SPM 和主要阳离子浓度的增加而增加,而胶体态 Fe 和 Mn 的百分比则随着河流的流动而减少。胶体和颗粒(来自非过滤水样)的透射电子显微镜分析表明,富 Fe 和 Mn 的天然纳米颗粒和天然有机物与颗粒相的异聚是主要机制。异聚控制着 Fe 和 Mn 在不同相中的分配,这可能是由于下游离子强度和二价阳离子浓度以及 SPM 浓度的增加所致。这些发现意味着 SPM 浓度在控制不同粒径分数中 Fe 和 Mn 的命运和行为方面起着重要作用。
图形摘要
(Fe-Mn)化合物的异聚形态:高 [SPM] → [Fe-Mn] 颗粒相;低 [SPM] → [Fe-Mn] 胶体-溶解相。