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Related Concept Videos

The Nitrogen Cycle01:49

The Nitrogen Cycle

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Nitrogen atoms, present in all proteins and DNA, are recycled between abiotic and biotic components of the ecosystem. However, the primary form of nitrogen on Earth is nitrogen gas, which cannot be used by most animals and plants. Thus, nitrogen gas must first be converted into a usable form by nitrogen-fixing bacteria before it can be cycled through other living organisms. The use of nitrogen-containing fertilizers and animal waste products in human agriculture has greatly influenced the...
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Related Experiment Video

Updated: Sep 6, 2025

Estimating Sediment Denitrification Rates Using Cores and N2O Microsensors
07:59

Estimating Sediment Denitrification Rates Using Cores and N2O Microsensors

Published on: December 6, 2018

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Predicting nitrous oxide emissions through riverine networks.

A Marzadri1, A Bellin1, J L Tank2

  • 1Department of Civil, Environmental and Mechanical Engineering, University of Trento, Trento, Italy.

The Science of the Total Environment
|June 24, 2022
PubMed
Summary
This summary is machine-generated.

Nitrous oxide (N2O) is a major ozone-depleting and greenhouse gas. A new model shows river N2O emissions depend on stream size, hydraulics, and morphology, not just nitrogen levels.

Keywords:
Dissolve inorganic nitrogenLand useN(2)O modelingNitrous oxide emissionsRiverine morphology

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Area of Science:

  • Environmental Science
  • Geochemistry
  • Hydrology

Background:

  • Nitrous oxide (N2O) is a significant ozone-depleting and greenhouse gas.
  • Predicting riverine N2O emissions is challenging, often relying on dissolved inorganic nitrogen (DIN) levels.
  • River hydromorphology also influences N2O emissions, but is less incorporated into predictive models.

Purpose of the Study:

  • To develop a predictive model for N2O concentrations and emissions at the river reach scale.
  • To incorporate biogeochemical and hydromorphological characteristics into N2O emission predictions.
  • To explain variations in N2O emissions across different river sizes and conditions.

Main Methods:

  • Developed a predictive model for riverine N2O concentrations and emissions.
  • Utilized Damköhler numbers to integrate reach-scale biogeochemical and hydromorphological factors.
  • Analyzed N2O emissions across varying river sizes, biomes, land use, climate, and nutrient availability.

Main Results:

  • The proposed model effectively predicts N2O concentrations and emissions at the reach scale.
  • Damköhler numbers capture key influences of river hydraulics and morphology on N2O emissions.
  • Dimensionless N2O concentrations and emission rates are more variable and higher in small streams (<10 m width) compared to larger rivers.

Conclusions:

  • River size, hydraulics, and morphology are critical factors influencing N2O emissions.
  • The model provides a more comprehensive understanding of riverine N2O dynamics than DIN-based regressions alone.
  • Small streams exhibit greater variability in N2O emissions due to complex spatial variations in hydraulics and morphology.