Linking seasonal N2O emissions and nitrification failures to microbial dynamics in a SBR wastewater treatment plant

Wenzel Gruber; Robert Niederdorfer; Jörg Ringwald; Eberhard Morgenroth; Helmut Bürgmann; Adriano Joss

doi:10.1016/j.wroa.2021.100098

Linking seasonal N₂O emissions and nitrification failures to microbial dynamics in a SBR wastewater treatment plant

Water Res X. 2021 Mar 22:11:100098. doi: 10.1016/j.wroa.2021.100098. eCollection 2021 May 1.

Authors

Wenzel Gruber^{1

2}, Robert Niederdorfer³, Jörg Ringwald⁴, Eberhard Morgenroth^{1

2}, Helmut Bürgmann³, Adriano Joss¹

Affiliations

¹ Eawag, Swiss Federal Institute for Aquatic Science and Technology, 8600 Duebendorf, Switzerland.
² Institute of Environmental Engineering, ETH Zürich, 8093 Zürich, Switzerland.
³ Eawag, Swiss Federal Institute for Aquatic Science and Technology, 6047 Kastanienbaum, Switzerland.
⁴ ARA Jungholz, Seestrasse 171, 8610 Uster, Switzerland.

Abstract

Nitrous oxide (N₂O) is a strong greenhouse gas and causal for stratospheric ozone depletion. During biological nitrogen removal in wastewater treatment plants (WWTP), high N₂O fluxes to the atmosphere can occur, typically exhibiting a seasonal emission pattern. Attempts to explain the peak emission phases in winter and spring using physico-chemical process data from WWTP were so far unsuccessful and new approaches are required. The complex and diverse microbial community of activated sludge used in biological treatment systems also exhibit substantial seasonal patterns. However, a potentially causal link between the seasonal patterns of microbial diversity and N₂O emissions has not yet been investigated. Here we show that in a full-scale WWTP nitrification failure and N₂O peak emissions, bad settleability of the activated sludge and a turbid effluent strongly correlate with a significant reduction in the microbial community diversity and shifts in community composition. During episodes of impaired performance, we observed a significant reduction in abundance for filamentous and nitrite oxidizing bacteria in all affected reactors. In some reactors that did not exhibit nitrification and settling failures, we observed a stable microbial community and no drastic loss of species. Standard engineering approaches to stabilize nitrification, such as increasing the aerobic sludge age and oxygen availability failed to improve the plant performance on this particular WWTP and replacing the activated sludge was the only measure applied by the operators to recover treatment performance in affected reactors. Our results demonstrate that disturbances of the sludge microbiome affect key structural and functional microbial groups, which lead to seasonal N₂O emission patterns. To reduce N₂O emissions from WWTP, it is therefore crucial to understand the drivers that lead to the microbial population dynamics in the activated sludge.

Keywords: Activated sludge microbiome; Amplicon sequencing; Denitrification; Nitrification; Physico-chemical monitoring.