<p>Agricultural drainage ditches have been recently identified as hotspots of methane (CH<sub>4</sub>), carbon dioxide (CO<sub>2</sub>), and nitrous oxide (N<sub>2</sub>O) emissions. Ditches often experience inputs of fertilizers from adjacent agricultural fields, which increases the availability of organic carbon and nutrients in ditch sediments, thereby fueling greenhouse gas (GHG) production. Here, we quantify the effects of two types of fertilizers (manure and artificial fertilizer) on GHG dynamics from agricultural drainage ditch sediments subjected to oxic and anoxic conditions. We first measured rates of potential sediment N<sub>2</sub>O production, CH<sub>4</sub> production, and aerobic CH<sub>4</sub> oxidation under different fertilizer doses. We observed that manure additions (expressed here as ammonium (NH<sub>4</sub><sup>+</sup>) dose, referring to the resulting NH<sub>4</sub><sup>+</sup> concentration in a given bottle after addition) strongly stimulated CH<sub>4</sub> and N<sub>2</sub>O production. Methane production rates increased approximately threefold as a result of manure additions, ranging from 18.4 to 61.7&#xa0;µmol CH<sub>4</sub> gDW<sup>−1</sup> d<sup>−1</sup>, whereas N<sub>2</sub>O production rates increased approximately 16-fold, and varied from 0.1 to 1.6&#xa0;µmol N<sub>2</sub>O gDW<sup>−1</sup> d<sup>−1</sup> across manure doses. Aerobic CH<sub>4</sub> oxidation was also stimulated by manure addition, while at resulting NH<sub>4</sub><sup>+</sup> concentrations above 2&#xa0;mmol L<sup>−1</sup>, oxidation rates declined. In contrast, artificial fertilizer caused immediate inhibition of CH<sub>4</sub> and N<sub>2</sub>O production and aerobic CH<sub>4</sub> oxidation, even at the lowest NH<sub>4</sub><sup>+</sup> concentration tested (0.05&#xa0;mmol L<sup>−1</sup>). Focusing on the effects of manure on GHG emissions, we observed that under anoxic conditions, sediment cores receiving high manure inputs emitted approximately 3.5 times more GHGs (in CO<sub>2</sub>-equivalents) than anoxic controls (no manure) and about 5.5 times more than oxic controls. Methane was the dominant driver of increased emissions at higher manure doses. As fertilizer use continues to rise globally, these results highlight the importance of implementing climate-smart water and nutrient management strategies in ditches and adjacent grasslands to mitigate climate trade-offs.</p>

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Manure application magnifies methane emission from drainage ditch sediments

  • Quinten Struik,
  • Madison Cicha,
  • José R. Paranaíba,
  • Sarian Kosten,
  • Annelies J. Veraart

摘要

Agricultural drainage ditches have been recently identified as hotspots of methane (CH4), carbon dioxide (CO2), and nitrous oxide (N2O) emissions. Ditches often experience inputs of fertilizers from adjacent agricultural fields, which increases the availability of organic carbon and nutrients in ditch sediments, thereby fueling greenhouse gas (GHG) production. Here, we quantify the effects of two types of fertilizers (manure and artificial fertilizer) on GHG dynamics from agricultural drainage ditch sediments subjected to oxic and anoxic conditions. We first measured rates of potential sediment N2O production, CH4 production, and aerobic CH4 oxidation under different fertilizer doses. We observed that manure additions (expressed here as ammonium (NH4+) dose, referring to the resulting NH4+ concentration in a given bottle after addition) strongly stimulated CH4 and N2O production. Methane production rates increased approximately threefold as a result of manure additions, ranging from 18.4 to 61.7 µmol CH4 gDW−1 d−1, whereas N2O production rates increased approximately 16-fold, and varied from 0.1 to 1.6 µmol N2O gDW−1 d−1 across manure doses. Aerobic CH4 oxidation was also stimulated by manure addition, while at resulting NH4+ concentrations above 2 mmol L−1, oxidation rates declined. In contrast, artificial fertilizer caused immediate inhibition of CH4 and N2O production and aerobic CH4 oxidation, even at the lowest NH4+ concentration tested (0.05 mmol L−1). Focusing on the effects of manure on GHG emissions, we observed that under anoxic conditions, sediment cores receiving high manure inputs emitted approximately 3.5 times more GHGs (in CO2-equivalents) than anoxic controls (no manure) and about 5.5 times more than oxic controls. Methane was the dominant driver of increased emissions at higher manure doses. As fertilizer use continues to rise globally, these results highlight the importance of implementing climate-smart water and nutrient management strategies in ditches and adjacent grasslands to mitigate climate trade-offs.