20Nitrification, the oxidative process converting ammonia to nitrite and nitrate, is driven by microbes 21 and plays a central role in the global nitrogen cycle. Our earlier metagenomics, amoA-amplicon, and 22 amoA-qPCR based investigations of groundwater-fed biofilters indicated a consistently high 23 abundance of comammox Nitrospira, and we hypothesized that these non-classical nitrifiers drive 24 ammonia-N oxidation. Hence, we used DNA and RNA stable isotope probing (SIP) coupled with 25 16S rRNA amplicon sequencing to identify the active members in the biofilter community when 26 subject to a continuous supply of NH4 + or NO2in the presence of 13 C-HCO3 -(labelled) or 12 C-HCO3 -27 (unlabelled). Allylthiourea (ATU) and sodium chlorate were added to inhibit autotrophic ammonia-28 and nitrite-oxidizing bacteria, respectively. Our results confirmed that lineage II Nitrospira 29 dominated ammonium oxidation in the biofilter community. A total of 78 (8 in RNA-SIP and 70 in 30 DNA-SIP) and 96 (25 in RNA-SIP and 71 in DNA-SIP) Nitrospira phylotypes (at 99% 16S rRNA 31 sequence similarity) were identified as complete ammonia-and nitrite-oxidizing, respectively. We 32 also detected significant HCO3uptake by Acidobacteria subgroup10, Pedomicrobium, Rhizobacter, 33 and Acidovorax under conditions that favoured ammonium oxidation. Canonical Nitrospira alone 34 drove nitrite oxidation in the biofilter community, and activity of archaeal ammonia oxidizing taxa 35 was not detected in the SIP fractions. This study provides the first in-situ evidence of ammonia 36 oxidation by comammox Nitrospira in an ecologically relevant complex microbiome.
38Nitrification, the stepwise oxidation of ammonia (NH3) to nitrite (NO2 -) and nitrate (NO3 -), supplies 40 the substrates for processes that initiate the loss of reactive nitrogen from the biosphere as N2. 41 Understanding the organisms and environmental controls that drive nitrification is important as it 42 controls global homeostasis of the N cycle. In engineered environments, complete nitrification is 43 often desired: this is essential when waters are prepared and distributed for human consumption. 44 Residual NH3 or NO2 --the result of incomplete nitrification -renders the water biologically unstable 45 and unsafe for human consumption. Hence, biological systems for source water treatment are 46 contingent on nitrifying prokaryotes. Based on evolutionarily conserved taxonomic (small subunit, 47 16S rRNA) and functional (e.g. ammonia monooxygenase, amoA) gene surveys, Nitrosomonas (1-48 4), Nitrosoarchaeum, and Nitrososphaera have been identified as the abundant ammonium oxidizing 49 prokaryotes (AOP) and Nitrospira (5, 6) as the abundant nitrite oxidizing prokaryotes (NOP) in 50 drinking water treatment systems, consistent with the classical assumption of division of labor in the 51 two nitrification steps.
52Our previous studies on rapid gravity sand filters (RGSF), used in potable water preparation from 53 groundwater, revealed nitrifying microbial communi...