Highlights 10• Microbial distribution was mainly influenced by sampling location within the DWTP.• Clade A comammox Nitrospira were the most abundant nitrifying guild in samples from the primary sand filter, while clade B dominated in samples from wall biofilm and the secondary filter.• A novel methanotrophic bacterium affiliated with the Methylophilaceae family comprised 15 the largest bacterial fraction in the primary sand filter.
AbstractElevated concentrations of ammonium and methane in groundwater can cause severe problems during drinking water production. To avoid their accumulation, raw water in the Netherlands, and many other countries, is purified by sand filtration. These drinking water filtration systems select 20 for microbial communities that mediate the biodegradation of organic and inorganic compounds.In this study, the active layers and wall biofilm of a Dutch drinking water treatment plant (DWTP) were sampled at different locations along the filtration units of the plant over three years. We used high-throughput sequencing in combination with differential coverage and sequence compositionbased binning to recover 56 near-complete metagenome-assembled genomes (MAGs) with an 25 estimated completion of ≥70% and with ≤10% redundancy. These MAGs were used to characterize the microbial communities involved in the conversion of ammonia and methane. The methanotrophic microbial communities colonizing the wall biofilm (WB) and the granular material of the primary rapid sand filter (P-RSF) were dominated by members of the Methylococcaceae and Methylophilaceae. The abundance of these bacteria drastically decreased in the secondary 30 rapid sand filter (S-RSF) samples. In all samples, complete ammonia-oxidizing (comammox) Nitrospira were the most abundant nitrifying guild. Clade A comammox Nitrospira dominated the P-RSF, while clade B was most abundant in WB and S-RSF, where ammonium concentrations were much lower. In conclusion, the knowledge obtained in this study contributes to understanding the role of microorganisms in the removal of carbon and nitrogen compounds during drinking 35 water production. We furthermore found that drinking water treatment plants represent valuable model systems to study microbial community function and interaction.
Methane uptakeMethane-oxidizing capacity was determined for the P-RSF and WB samples collected in 2016. 115For the P-RSF, 2.5, 5, 10, and 20 g of sand material were mixed with 20 ml top water. After settling of the sand, overlaying water samples (20 ml) were transferred into 120 ml serum bottles with Deep aquifer Clay Shallow aquifer Sand and gravel NH 4 + CH 4 Fe H 2 S Mn Groundwater Air supply Air supply WB P-RSF S-RSF Storage and distribution Wall