Effects of sulfur on nitrogen transformation in malodorous rivers with different remediations

High levels of total nitrogen (TN) in urban rivers remain a significant environmental concern due to their contribution to malodor, which needs an urgent solution. Considering the critical role of sulfur (S) in river habitats, how and to what extent S is involved in nitrogen (N) transformation deserves attention, especially in the context of river remediations. In this study, sediment incubation and river simulation showed that denitrification had a higher tolerance to sulfide than anaerobic ammonium oxidation (anammox) and outcompeted anammox in substrate competition. Moreover, appropriate levels of sulfide (40 mg·L<sup>-1</sup>) stimulated S-driven autotrophic denitrification (SAD) activity (from 0.010 to 0.021 meq·g<sup>-1</sup> VSS·h<sup>-1</sup>), with the relative abundances of Thiobacillus-like bacteria increasing from 0.46% to 21.51%. However, 40 mg·L<sup>-1</sup> sulfide inhibited anammox activity (from 0.010 to 0.0032 meq·g<sup>-1</sup> VSS·h<sup>-1</sup>), with the decrease in both ammonium removal (from 55.25% to 22.32%) and anammox bacteria abundance (from 0.45% to 0.18%) in the incubation. A significant correlation (P < 0.01) between TN and sulfate was observed in calcium nitrate added and aerated river simulations, which indicated that sulfide was involved in the N-transformation through SAD. This finding was further confirmed by the relatively high abundances of Thiobacillus (1.15% and 1.12%, respectively) in both sediment aeration and calcium nitrate addition systems. Notably, S-driven autotrophic partial denitrification coupled with anammox was discovered under calcium nitrate addition. This study can fill the gap in understanding the interactions of S and N biogeochemical processes with river remediations and can help establish an effective approach for TN removal. KEY POINTS: • Anammox showed higher sensitivity to 40 mg·L<sup>-1</sup> sulfide than denitrification. • Coupling mechanisms between S and N were studied based on real river scenario. • Calcium nitrate induced the coupling of SAPD with anammox. • Denitrification showed relatively high tolerance to sulfide in malodorous rivers.

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Publication Details

Journal
Applied Microbiology and Biotechnology
Published
2025-10-25
DOI
https://doi.org/10.1007/s00253-025-13612-0
Citations
2
Primary Topic
Wastewater Treatment and Nitrogen Removal
Type
article
Field-Weighted Citation Impact
1.01

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article

Effects of sulfur on nitrogen transformation in malodorous rivers with different remediations

Gongming Zhou, Yunyi Zha, Chu-Chun Yu, Yao Huang et al.
2 citations
Applied Microbiology and Biotechnology
Wastewater Treatment and Nitrogen Removal
1.01
article

Effects of sulfur on nitrogen transformation in malodorous rivers with different remediations

Gongming Zhou, Yunyi Zha, Chu-Chun Yu, Yao Huang, Yan He, Jin Zhu
article en
2 citations

Abstract

High levels of total nitrogen (TN) in urban rivers remain a significant environmental concern due to their contribution to malodor, which needs an urgent solution. Considering the critical role of sulfur (S) in river habitats, how and to what extent S is involved in nitrogen (N) transformation deserves attention, especially in the context of river remediations. In this study, sediment incubation and river simulation showed that denitrification had a higher tolerance to sulfide than anaerobic ammonium oxidation (anammox) and outcompeted anammox in substrate competition. Moreover, appropriate levels of sulfide (40 mg·L<sup>-1</sup>) stimulated S-driven autotrophic denitrification (SAD) activity (from 0.010 to 0.021 meq·g<sup>-1</sup> VSS·h<sup>-1</sup>), with the relative abundances of Thiobacillus-like bacteria increasing from 0.46% to 21.51%. However, 40 mg·L<sup>-1</sup> sulfide inhibited anammox activity (from 0.010 to 0.0032 meq·g<sup>-1</sup> VSS·h<sup>-1</sup>), with the decrease in both ammonium removal (from 55.25% to 22.32%) and anammox bacteria abundance (from 0.45% to 0.18%) in the incubation. A significant correlation (P < 0.01) between TN and sulfate was observed in calcium nitrate added and aerated river simulations, which indicated that sulfide was involved in the N-transformation through SAD. This finding was further confirmed by the relatively high abundances of Thiobacillus (1.15% and 1.12%, respectively) in both sediment aeration and calcium nitrate addition systems. Notably, S-driven autotrophic partial denitrification coupled with anammox was discovered under calcium nitrate addition. This study can fill the gap in understanding the interactions of S and N biogeochemical processes with river remediations and can help establish an effective approach for TN removal. KEY POINTS: • Anammox showed higher sensitivity to 40 mg·L<sup>-1</sup> sulfide than denitrification. • Coupling mechanisms between S and N were studied based on real river scenario. • Calcium nitrate induced the coupling of SAPD with anammox. • Denitrification showed relatively high tolerance to sulfide in malodorous rivers.

Applied Microbiology and BiotechnologyVol. 109(1)
Tongji University (CN), Shanxi University (CN), State Key Laboratory of Pollution Control and Resource Reuse (CN), East China Normal University (CN)
National Natural Science Foundation of China, Fundamental Research Funds for the Central Universities
Openalex Percentile: Top 22%
Wastewater Treatment and Nitrogen Removal
1.01
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