Fertilizer timing affects nitrous oxide, carbon dioxide, and ammonia emissions from soil

The impact of interactions between management and climate on nitrous oxide (N2O), carbon dioxide (CO2), and ammonia (NH3) emissions are not well understood. This study quantified the effect of urea fertilizer application timing on inorganic N movement, immobilization, and the gaseous emissions of N2...

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Veröffentlicht in:Soil Science Society of America journal 2020-01, Vol.84 (1), p.115-130
Hauptverfasser: Thies, Samuel, Joshi, Deepak R., Bruggeman, Stephanie A., Clay, Sharon A., Mishra, Umakant, Morile‐Miller, Janet, Clay, David E.
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container_issue 1
container_start_page 115
container_title Soil Science Society of America journal
container_volume 84
creator Thies, Samuel
Joshi, Deepak R.
Bruggeman, Stephanie A.
Clay, Sharon A.
Mishra, Umakant
Morile‐Miller, Janet
Clay, David E.
description The impact of interactions between management and climate on nitrous oxide (N2O), carbon dioxide (CO2), and ammonia (NH3) emissions are not well understood. This study quantified the effect of urea fertilizer application timing on inorganic N movement, immobilization, and the gaseous emissions of N2O‐N, CO2‐C, and NH3‐N. Urea was applied once, at two rates (0 and 224 kg ha−1) on six dates (early fall, 20 Sept. 2017; mid‐fall, 11 Oct. 2017; early winter, 1 Nov. 2017; early spring, 1 May 2018; mid‐spring, 22 May 2018; and early summer, 12 June 2018). Gaseous emissions, soil temperature, and soil moisture were measured every 4 h for 21 consecutive days following urea application. Changes in soil inorganic N contents were used to determine the amount of inorganic N remaining in the soil, nitrification, immobilization/fixation, and leaching. For all fertilizer application dates, the cumulative fertilizer derived N2O‐N emissions for the 21 days following application were 60%). These findings indicate that intergovernmental panel on climate change (IPCC) default value of 1% of applied N for N2O emissions improved by considering the fertilizer application date.
doi_str_mv 10.1002/saj2.20010
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This study quantified the effect of urea fertilizer application timing on inorganic N movement, immobilization, and the gaseous emissions of N2O‐N, CO2‐C, and NH3‐N. Urea was applied once, at two rates (0 and 224 kg ha−1) on six dates (early fall, 20 Sept. 2017; mid‐fall, 11 Oct. 2017; early winter, 1 Nov. 2017; early spring, 1 May 2018; mid‐spring, 22 May 2018; and early summer, 12 June 2018). Gaseous emissions, soil temperature, and soil moisture were measured every 4 h for 21 consecutive days following urea application. Changes in soil inorganic N contents were used to determine the amount of inorganic N remaining in the soil, nitrification, immobilization/fixation, and leaching. For all fertilizer application dates, the cumulative fertilizer derived N2O‐N emissions for the 21 days following application were &lt;0.05% of the applied N. Fertilizer‐derived N2O‐N emission rates were higher than N2O‐N emission rates in the unfertilized soil in early fall and early summer. Even though the highest net N2O‐N emissions occurred in early spring, the application of fertilizer did not increase emissions. The highest net N2O‐N + NH3‐N emissions occurred in cool soils (early spring) in soils with water filled pore space (&gt;60%). 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This study quantified the effect of urea fertilizer application timing on inorganic N movement, immobilization, and the gaseous emissions of N2O‐N, CO2‐C, and NH3‐N. Urea was applied once, at two rates (0 and 224 kg ha−1) on six dates (early fall, 20 Sept. 2017; mid‐fall, 11 Oct. 2017; early winter, 1 Nov. 2017; early spring, 1 May 2018; mid‐spring, 22 May 2018; and early summer, 12 June 2018). Gaseous emissions, soil temperature, and soil moisture were measured every 4 h for 21 consecutive days following urea application. Changes in soil inorganic N contents were used to determine the amount of inorganic N remaining in the soil, nitrification, immobilization/fixation, and leaching. For all fertilizer application dates, the cumulative fertilizer derived N2O‐N emissions for the 21 days following application were &lt;0.05% of the applied N. Fertilizer‐derived N2O‐N emission rates were higher than N2O‐N emission rates in the unfertilized soil in early fall and early summer. Even though the highest net N2O‐N emissions occurred in early spring, the application of fertilizer did not increase emissions. The highest net N2O‐N + NH3‐N emissions occurred in cool soils (early spring) in soils with water filled pore space (&gt;60%). 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source Wiley Online Library Journals Frontfile Complete
subjects ammonia
application timing
autumn
carbon dioxide
climate
fertilizer application
nitrification
nitrous oxide
soil temperature
soil water
spring
summer
United Nations Framework Convention on Climate Change
urea
urea fertilizers
winter
title Fertilizer timing affects nitrous oxide, carbon dioxide, and ammonia emissions from soil
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