Author:
Juncosa Ricardo,Delgado Jorge,Cereijo José Luis,Muñoz Andrea
Abstract
AbstractThe formation of natural lakes is a process that takes place over thousands of years, although the volumetric formation depends on hydrological and climatological phenomena, reaching a stationary hydraulic regime, the evolution of hydrochemistry is more complex and obeys not only phenomena of stoichiometry and chemical kinetics but also diffusion processes. Depending on the depth of the lakes, the anoxization process originating from the bottom is the first phase of the lake’s methanogenesis. For this, the course of many thousands of years is necessary, so the studies carried out in the lakes are limited to the current knowledge of the state in which they are, without being able to have real information in this process of methanogenesis. There are no data available on the generation process of a natural lake in its primary stages. In this case, taking advantage of the rehabilitation of the old open-pit mining of Meirama (Northwest Spain), consisting of the controlled flooding of the hole by groundwater, by stopping the perimeter pumping, and the derivation of the nearby streams, whose contribution was the majority with respect to the subterranean contribution, there has been the opportunity to physically and chemically monitor the complete filling of the said hole. The present study focuses on the analysis of the evolution of the different processes initiated in the methanogenesis of the lake bottom identified in the well-known Redox ladder: obtaining oxygen from the reduction of nitrogenous compounds and metallic oxides, from the reduction of the sulfate and the generation of methane from carbon compounds, the latter phase without reaching. Although the methanization process is very slow, it has had the opportunity to know the formation of a lake at its origin, from the hydrochemical point of view. It has been possible to verify that the methanization processes at the bottom, given the anoxia conditions, are in a very primitive phase with the reduction of nitrate and nitrite to ammonium and beginning a reduction of metal oxides and sulfate.
Publisher
Springer Science and Business Media LLC
Subject
Management, Monitoring, Policy and Law,Pollution,General Environmental Science,General Medicine
Reference46 articles.
1. APHA. (1998). Standard methods for the examination of water and wastewater. 20th edition (p. 1220). American Public Health Association, American Water Works Association, Water Environment Federation.
2. Appelo, C. A. J., & Postma, D. (1992). Geochemistry, groundwater, and pollution (p. 536). Ed. Balkema.
3. Bachmann, T. M., Friese, K., & Zachmann, D. W. (2001). Redox and ph conditions in the water column and in the sediments of an acidic mining lake. Journal of Geochemical Exploration, 73(2), 75–86. https://doi.org/10.1016/S0375-6742(01)00189-3
4. Bylak, A., Rak, W., Wójcik, M., Kukuła, E., & Kukuła, K. (2019). Analysis of macrobenthic communities in a post-mining sulphur pit lake (Poland). Mine Water Environ., 38, 536–550.
5. Carlson, R. E. (1977). A trophic state index for lakes. Limnology and Oceanography, 22, 361–369.
Cited by
2 articles.
订阅此论文施引文献
订阅此论文施引文献,注册后可以免费订阅5篇论文的施引文献,订阅后可以查看论文全部施引文献