Influence of filter age on Fe, Mn and NH4+ removal in dual media rapid sand filters used for drinking water production

•Newly started rapid sand filters fail to remove Mn and NH4+.•Filters of intermediate age with thin metal coatings remove Mn and NH4+ optimally.•The nitrifying community changes with filter age.•Despite the presence of Gallionella, Fe2+ removal is mostly chemical.•Suboptimal Mn removal in old filter...

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Veröffentlicht in:Water research (Oxford) 2023-08, Vol.242, p.120184-120184, Article 120184
Hauptverfasser: Haukelidsaeter, Signe, Boersma, Alje S., Kirwan, Liam, Corbetta, Alessia, Gorres, Isaac D., Lenstra, Wytze K., Schoonenberg, Frank K., Borger, Karl, Vos, Luuk, van der Wielen, Paul W.J.J., van Kessel, Maartje A.H.J., Lücker, Sebastian, Slomp, Caroline P.
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Sprache:eng
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Zusammenfassung:•Newly started rapid sand filters fail to remove Mn and NH4+.•Filters of intermediate age with thin metal coatings remove Mn and NH4+ optimally.•The nitrifying community changes with filter age.•Despite the presence of Gallionella, Fe2+ removal is mostly chemical.•Suboptimal Mn removal in old filters is attributed to preferential flow. Rapid sand filtration is a common method for removal of iron (Fe), manganese (Mn) and ammonium (NH4+) from anoxic groundwaters used for drinking water production. In this study, we combine geochemical and microbiological data to assess how filter age influences Fe, Mn and NH4+ removal in dual media filters, consisting of anthracite overlying quartz sand, that have been in operation for between ∼2 months and ∼11 years. We show that the depth where dissolved Fe and Mn removal occurs is reflected in the filter medium coatings, with ferrihydrite forming in the anthracite in the top of the filters (< 1 m), while birnessite-type Mn oxides are mostly formed in the sand (> 1 m). Removal of NH4+ occurs through nitrification in both the anthracite and sand and is the key driver of oxygen loss. Removal of Fe is independent of filter age and is always efficient (> 97% removal). In contrast, for Mn, the removal efficiency varies with filter age, ranging from 9 to 28% at ∼2–3 months after filter replacement to 100% after 8 months. After 11 years, removal reduces to 60–80%. The lack of Mn removal in the youngest filters (at 2–3 months) is likely the result of a relatively low abundance of mineral coatings that adsorb Mn2+ and provide surfaces for the establishment of a microbial community. 16S rRNA gene amplicon sequencing shows that Gallionella, which are known Fe2+ oxidizers, are present after 2 months, yet Fe2+ removal is mostly chemical. Efficient NH4+ removal (> 90%) establishes within 3 months of operation but leakage occurs upon high NH4+loading (> 160 µM). Two-step nitrification by Nitrosomonas and Candidatus Nitrotoga is likely the most important NH4+ removal mechanism in younger filters during ripening (2 months), after which complete ammonia oxidation by Nitrospira and canonical two-step nitrification occur simultaneously in older filters. Our results highlight the strong effect of filter age on especially Mn2+but also NH4+ removal. We show that ageing of filter medium leads to the development of thick coatings, which we hypothesize leads to preferential flow, and breakthrough of Mn2+. Use of age-specific flow rates may increase
ISSN:0043-1354
1879-2448
DOI:10.1016/j.watres.2023.120184