共 7 条
Influence of filter age on Fe, Mn and NH4+ removal in dual media rapid sand filters used for drinking water production
被引:16
|作者:
Haukelidsaeter, Signe
[1
]
Boersma, Alje S.
[2
]
Kirwan, Liam
[1
]
Corbetta, Alessia
[1
]
Gorres, Isaac D.
[2
]
Lenstra, Wytze K.
[1
]
Schoonenberg, Frank K.
[3
]
Borger, Karl
[3
]
Vos, Luuk
[4
]
van der Wielen, Paul W. J. J.
[4
,5
]
van Kessel, Maartje A. H. J.
[2
]
Lucker, Sebastian
[2
]
Slomp, Caroline P.
[1
,2
]
机构:
[1] Univ Utrecht, Fac Geosci, Dept Earth Sci, POB 80021, NL-3508 TA Utrecht, Netherlands
[2] Radboud Univ Nijmegen, Radboud Inst Biol & Environm Sci, Fac Sci, Dept Microbiol, POB 9010, NL-6500 GL Nijmegen, Netherlands
[3] Vitens NV, POB 1205, NL-8001 BE Zwolle, Netherlands
[4] KWR Water Res Inst, POB 1072, NL-3430 BB Nieuwegein, Netherlands
[5] Wageningen Univ & Res, Lab Microbiol, Stippeneng 4, NL-6708 WE Wageningen, Netherlands
来源:
基金:
欧洲研究理事会;
关键词:
MANGANESE REMOVAL;
MICROBIAL COMMUNITIES;
POTABLE WATER;
IRON;
NITRIFICATION;
ADSORPTION;
OXIDATION;
D O I:
10.1016/j.watres.2023.120184
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
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 similar to 2 months and similar to 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 similar to 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 mu M). 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 the contact time with the filter medium in older filters and improve Mn2+ and NH4+ removal.
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