Mechanisms of Nitrate Concentration Effects on N₂O and N₂ Fluxes Across Different River Widths

Authors

  • Zitong Shao
  • Jiarui Du
  • Hao Wang

DOI:

https://doi.org/10.54691/stwek692

Keywords:

Nitrate Concentration; River Width; N₂O Flux; N₂ Flux; Denitrifying Microorganisms; Nitrogen Cycle; Benthic Niche; qPCR.

Abstract

This study systematically investigated the mechanisms by which nitrate concentrations influence N₂O and N₂ fluxes in rivers of varying widths (20–800 m) within the Haihe River Basin, Luanhe River Basin, and independent rivers flowing into the sea in the Beijing-Tianjin-Hebei region. Through a combination of field sampling and laboratory analysis, nitrate concentrations and gas fluxes at the sediment-water interface were measured, while qPCR technology was employed to analyze the abundance of nitrogen-functioning microbial genes. Results indicate that nitrate concentration significantly influences N₂O and N₂ fluxes by providing denitrification substrates and regulating microbial community structure. River width further modulates nitrate influence intensity and pathways by altering water dilution capacity and microbial habitat. Narrow rivers exhibit heightened sensitivity to nitrate, yielding higher gas fluxes, whereas wide rivers promote nitrate conversion to N₂ due to dilution effects and stable environments. This study provides microbial mechanism-level insights into understanding river nitrogen cycling and its environmental effects.

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References

[1] Li Ya, Li Huilan, Li Hengliang, et al. Study on the Determination of Nitrite Nitrogen, Nitrate Nitrogen, Ammonia Nitrogen, and Total Nitrogen in Freshwater Using Continuous Flow Analysis [J]. Environmental Protection and Circular Economy, 2024, 44(03): 77-84.China National Standardization Management Committee. Specifications of Crane Design (China Standardization Press, China 2008), p. 16-19.

[2] J Wang Juan, Wang Hongqiong, Li Yejun. Discussion on Methods for Measuring Nitrate Ions in Groundwater of Xining Region [J]. Science and Technology Innovation and Application, 2013,(22):62. DOI:10.19981/j.cn23-1581/g3.2013.22.050.Q. D. Zeng, Q. E. Li: Progress in Civil Engineering, Vol. 32 (2012) No. 9, p. 3077-3080.

[3] Jia Yunjiao. Phosphoric Acid Activation of Traditional Chinese Medicine Residues for Self-Pressurized Low-Temperature Carbonization Process and Product Performance Research [D]. Kunming University of Science and Technology, 2021. DOI:10.27200/d.cnki.gkmlu.2021.002317.

[4] Li, X. Z. Mechanisms of N₂O Production in Water-Sediment Systems of Weakly Hydrodynamic Rivers in Marine-Terrestrial Transition Zones [D]. Tianjin University, 2022. DOI:10.27356/d.cnki.gtjdu.2022.003884.

[5] Li Qianxia. Adaptability of dissimilatory nitrate-reducing bacteria (DNRA) to different carbon sources and their distribution in natural environments [D]. Shandong University, 2020. DOI:10.27272/d.cnki.gshdu.2020.002984.

[6] Li Yu. Screening of Denitrifying Gas-Producing Bacteria in Reservoirs and Their Gas-Producing Performance in Oil-Water Systems [D]. Qufu Normal University, 2022. DOI: 10.27267/d.cnki.gqfsu.2022.000961.

[7] Wan Xiaohong[1], Wang Qiwén[1], Wang Yuchun[1]. Study on N₂O Emission Characteristics in the Flood-Receding Zone of Zhuyi River, a Tributary of the Three Gorges Reservoir[J]. Environmental Protection Frontiers, 2018, 8(1):10. DOI:10.12677/AEP.2018.81011.

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Published

26-01-2026

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Section

Articles

How to Cite

Shao, Z., Du, J., & Wang, H. (2026). Mechanisms of Nitrate Concentration Effects on N₂O and N₂ Fluxes Across Different River Widths. Frontiers in Sustainable Development, 6(1), 23-27. https://doi.org/10.54691/stwek692