A difficult coexistence: Resolving the iron-induced nitrification delay in groundwater filters.

Autor: Corbera-Rubio F; Delft University of Technology, Delft, The Netherlands. Electronic address: f.corberarubio@tudelf.nl., Kruisdijk E; Delft University of Technology, Delft, The Netherlands., Malheiro S; Delft University of Technology, Delft, The Netherlands., Leblond M; Delft University of Technology, Delft, The Netherlands., Verschoor L; Delft University of Technology, Delft, The Netherlands., van Loosdrecht MCM; Delft University of Technology, Delft, The Netherlands., Laureni M; Delft University of Technology, Delft, The Netherlands., van Halem D; Delft University of Technology, Delft, The Netherlands.
Jazyk: angličtina
Zdroj: Water research [Water Res] 2024 Aug 15; Vol. 260, pp. 121923. Date of Electronic Publication: 2024 Jun 11.
DOI: 10.1016/j.watres.2024.121923
Abstrakt: Rapid sand filters (RSF) are an established and widely applied technology for the removal of dissolved iron (Fe 2+ ) and ammonium (NH 4 + ) among other contaminants in groundwater treatment. Most often, biological NH 4 + oxidation is spatially delayed and starts only upon complete Fe 2+ depletion. However, the mechanism(s) responsible for the inhibition of NH 4 + oxidation by Fe 2+ or its oxidation (by)products remains elusive, hindering further process control and optimization. We used batch assays, lab-scale columns, and full-scale filter characterizations to resolve the individual impact of the main Fe 2+ oxidizing mechanisms and the resulting products on biological NH 4 + oxidation. modeling of the obtained datasets allowed to quantitatively assess the hydraulic implications of Fe 2+ oxidation. Dissolved Fe 2+ and the reactive oxygen species formed as byproducts during Fe 2+ oxidation had no direct effect on ammonia oxidation. The Fe 3+ oxides on the sand grain coating, commonly assumed to be the main cause for inhibited ammonia oxidation, seemed instead to enhance it. modeling allowed to exclude mass transfer limitations induced by accumulation of iron flocs and consequent filter clogging as the cause for delayed ammonia oxidation. We unequivocally identify the inhibition of NH 4 + oxidizing organisms by the Fe 3+ flocs generated during Fe 2+ oxidation as the main cause for the commonly observed spatial delay in ammonia oxidation. The addition of Fe 3+ flocs inhibited NH 4 + oxidation both in batch and column tests, and the removal of Fe 3+ flocs by backwashing completely re-established the NH 4 + removal capacity, suggesting that the inhibition is reversible. In conclusion, our findings not only identify the iron form that causes the inhibition, albeit the biological mechanism remains to be identified, but also highlight the ecological importance of iron cycling in nitrifying environments.
Competing Interests: Declaration of competing interest The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: Francesc Corbera-Rubio reports financial support was provided by Vitens NV. Francesc Corbera-Rubio reports financial support was provided by Dunea Duin & Water.
(Copyright © 2024 The Author(s). Published by Elsevier Ltd.. All rights reserved.)
Databáze: MEDLINE
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