WLN, Rijksstraatweg 85, 9756 AD, Glimmen, The Netherlands; UNESCO-IHE Institute for Water Education, Westvest 7, 2611 AX, Delft, The Netherlands; Technical University Delft, Stevinweg 1, 2628 CN, Delft, The Netherlands.
UNESCO-IHE Institute for Water Education, Westvest 7, 2611 AX, Delft, The Netherlands.
Water Res. 2015 Feb 1;69:154-161. doi: 10.1016/j.watres.2014.11.019. Epub 2014 Nov 21.
The efficiency of manganese removal in conventional groundwater treatment consisting of aeration followed by rapid sand filtration, strongly depends on the ability of filter media to promote auto-catalytic adsorption of dissolved manganese and its subsequent oxidation. Earlier studies have shown that the compound responsible for the auto-catalytic activity in ripened filters is a manganese oxide called Birnessite. The aim of this study was to determine if the ripening of manganese removal filters and the formation of Birnessite on virgin sand is initiated biologically or physico-chemically. The ripening of virgin filter media in a pilot filter column fed by pre-treated manganese containing groundwater was studied for approximately 600 days. Samples of filter media were taken at regular time intervals, and the manganese oxides formed in the coating were analysed by Raman spectroscopy, Electron Paramagnetic Resonance (EPR) and Scanning Electron Microscopy (SEM). From the EPR analyses, it was established that the formation of Birnessite was most likely initiated via biological activity. With the progress of filter ripening and development of the coating, Birnessite formation became predominantly physico-chemical, although biological manganese oxidation continued to contribute to the overall manganese removal. The knowledge that manganese removal in conventional groundwater treatment is initiated biologically could be of help in reducing typically long ripening times by creating conditions that are favourable for the growth of manganese oxidizing bacteria.
在常规地下水处理中,锰的去除效率主要取决于过滤介质促进溶解锰自动催化吸附及其随后氧化的能力。早期的研究表明,在成熟滤器中负责自动催化活性的化合物是一种称为水钠锰矿的氧化锰。本研究旨在确定成熟除锰过滤器和原生砂上水钠锰矿的形成是由生物还是物理化学过程引发的。在一个用预处理含锰地下水进料的试验柱中,研究了原生滤料的成熟过程,大约持续了 600 天。定期取过滤介质样品,通过拉曼光谱、电子顺磁共振(EPR)和扫描电子显微镜(SEM)分析形成的锰氧化物。从 EPR 分析中可以确定,水钠锰矿的形成最有可能是通过生物活性引发的。随着过滤成熟和涂层的发展,尽管生物锰氧化继续为整体锰去除做出贡献,但水钠锰矿的形成主要是物理化学过程。了解到常规地下水处理中的锰去除是由生物引发的,这可能有助于通过创造有利于锰氧化菌生长的条件来缩短通常较长的成熟时间。