Abstract

Ammonia oxidation is the first step in nitrification and was thought to be performed solely by specialized bacteria. The discovery of ammonia-oxidizing archaea (AOA) changed this view. We examined the large scale and spatio-temporal occurrence, abundance and role of AOA throughout Chinese inland waters (n = 28). Molecular survey showed that AOA was ubiquitous in inland waters. The existence of AOA in extreme acidic, alkaline, hot, cold, eutrophic and oligotrophic environments expanded the tolerance limits of AOA, especially their known temperature tolerance to −25 °C, and substrate load to 42.04 mM. There were spatio-temporal divergences of AOA community structure in inland waters, and the diversity of AOA in inland water ecosystems was high with 34 observed species-level operational taxonomic units (OTUs; based on a 15% cutoff) distributed widely in group I.1b, I.1a, and I.1a-associated. The abundance of AOA was quite high (8.5 × 104 to 8.5 × 109 copies g−1), and AOA outnumbered ammonia-oxidizing bacteria (AOB) in the inland waters where little human activities were involved. On the whole AOB predominate the ammonia oxidation rate over AOA in inland water ecosystems, and AOA play an indispensable role in global nitrogen cycle considering that AOA occupy a broader habitat range than AOB, especially in extreme environments.

Highlights

  • Background of Inland WatersTypeSampled Environments and BackgroundsNumber Number of Number of of clones species-level SamplingIn situ samples sequencedoperational taxonomic units (OTUs) season temperature(°C)A: Longitudinal scale: from 86°06′ E to130°10′ E Tarim River41°03′ –41°04′ N, 86°06′ –86°07′ ERiparian The longest endorheic river in zoneChina and 5th in the world Summer

  • We examined the diversity of ammonia-oxidizing archaea (AOA) and differences among AOA community structures in the inland water ecosystems

  • The relative abundance of AOA compared with ammonia-oxidizing bacteria (AOB) varied throughout the sampling sites (Fig. 4). and AOA outnumbered AOB in almost all the lakes and rivers, while the opposite was true in the other inland waters with strong human activities such as paddy fields, reservoirs, polluted groundwater, tidal land and constructed wetland

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Summary

Objectives

The objectives of this study are to investigate the occurrence, biodiversity and distribution of AOA in inland water ecosystems through multiple samples, including those with extreme conditions, to broaden the known tolerance limits of AOA and to examine their ecological features

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