Nitrous oxide (N2O) flux responds exponentially to nitrogen fertilizer in irrigated wheat in the Yaqui Valley, Mexico

Abstract The Yaqui Valley, one of Mexico’s major breadbaskets, includes ∼230,000 ha of cultivated, irrigated cropland, with two thirds of the area planted annually to spring wheat (Triticum turgidum). Nitrogen (N) fertilizer applications to wheat have doubled since the 1980s, and currently average around 300 kg N ha−1. Emissions of nitrous oxide (N2O), a potent greenhouse gas, increase following soil management activities, especially irrigation when N fertilizer is applied, and particularly when N fertilizer inputs exceed crop N requirements. Here we investigate trade–offs among N fertilizer inputs, spring wheat yields, and N2O emissions to inform management strategies that can mitigate N2O emissions without compromising yields, and link this to how farmers can generate carbon credits from N management to receive payment for more precise N use. We used static chambers to measure N2O fluxes from spring wheat at five N fertilizer rates (0, 80, 160, 240, and 280 kg N ha−1) during two growing seasons at CIMMYT in Ciudad Obregon, Sonora, Mexico. Average daily fluxes were between 1.9 ± 0.5 and 13.4 ± 2.8 g N2O-N ha−1, with lower emissions at N rates below those that maximized yield, and substantially higher emissions at N rates beyond maximum yield; this exponential response is consistent with crops in temperate regions. Results suggest that current average N fertilizer rates (300 kg N ha−1) are at least double economically optimum rates, resulting in low crop N use efficiency: 36–39% at higher N rates as compared to 50–57% for economically optimum rates. N fertilizer rate reductions to the economic optimum rates here (123 and 145 kg N ha−1 in 2013 and 2014, respectively) could have avoided N2O emissions equivalent to 0.5 to 0.8 Mg CO2e ha−1 yr−1 or, regionally, 84–138 Gg CO2e yr−1 without harming yields. Insofar as fertilizer use in Yaqui Valley is likely similar to high-productivity irrigated cereal systems elsewhere, our results provide evidence for a global triple-win scenario: large reductions in agricultural GHG emissions, increased farmer income, and continued high productivity.

[1]  J. Zadoks A decimal code for the growth stages of cereals , 1974 .

[2]  Matson,et al.  Integration of environmental, agronomic, and economic aspects of fertilizer management , 1998, Science.

[3]  Impact of mineral N fertilizer application rates on N2O emissions from arable soils under winter wheat , 2014, Nutrient Cycling in Agroecosystems.

[4]  Stefano Schiavon,et al.  Climate Change 2007: The Physical Science Basis. , 2007 .

[5]  A. Bouwman Environmental science: Nitrogen oxides and tropical agriculture , 1998, Nature.

[6]  P. Rochette,et al.  N2O emissions from spring barley production as influenced by fertilizer nitrogen rate , 2008 .

[7]  P. Matson,et al.  DISTINGUISHING NITRIFICATION AND DENITRIFICATION SOURCES OF N2O IN A MEXICAN WHEAT SYSTEM USING 15N , 2000 .

[8]  Carolien Kroeze,et al.  The global nitrous oxide budget revisited , 2011 .

[9]  E. Davidson,et al.  Nitrogen Oxide Fluxes and Nitrogen Cycling during Postagricultural Succession and Forest Fertilization in the Humid Tropics , 2001, Ecosystems.

[10]  M. Hawkesford Reducing the reliance on nitrogen fertilizer for wheat production , 2014, Journal of cereal science.

[11]  K. Yagi,et al.  Nitrous oxide emissions from an intensively cultivated maize-wheat rotation soil in the North China Plain. , 2007, The Science of the total environment.

[12]  Timothy B. Parkin,et al.  Soil Microsites as a Source of Denitrification Variability1 , 1987 .

[13]  Johan Six,et al.  The potential to mitigate global warming with no‐tillage management is only realized when practised in the long term , 2004 .

[14]  C. Billow,et al.  Fertilization practices and soil variations control nitrogen oxide emissions from tropical sugar cane , 1996 .

[15]  David B. Lobell,et al.  Impacts of Day Versus Night Temperatures on Spring Wheat Yields: A Comparison of Empirical and CERES Model Predictions in Three Locations , 2007 .

[16]  Amy M. Marcarelli,et al.  Nitrogen Transformations , 2018, Handbook of Soil Sciences (Two Volume Set).

[17]  William R. Raun,et al.  Improving Nitrogen Use Efficiency for Cereal Production , 1999 .

[18]  G. Robertson,et al.  Global metaanalysis of the nonlinear response of soil nitrous oxide (N2O) emissions to fertilizer nitrogen , 2014, Proceedings of the National Academy of Sciences.

[19]  Keith Paustian,et al.  Agricultural soil greenhouse gas emissions: a review of national inventory methods. , 2006, Journal of environmental quality.

[20]  David B. Lobell,et al.  Analysis of wheat yield and climatic trends in Mexico , 2005 .

[21]  A. Dobermann,et al.  Agroecosystems, Nitrogen-use Efficiency, and Nitrogen Management , 2002, Ambio.

[22]  G. Robertson,et al.  Quantifying N2O emissions reductions in US agricultural crops through N fertilizer rate reduction , 2013 .

[23]  S. Hamilton,et al.  Nitrogen fertilization challenges the climate benefit of cellulosic biofuels , 2016 .

[24]  G. Marland,et al.  A synthesis of carbon sequestration, carbon emissions, and net carbon flux in agriculture: comparing tillage practices in the United States , 2002 .

[25]  S. Ogle,et al.  N2O emissions from managed soils, and CO2 emissions from lime and urea application , 2019 .

[26]  Peter Grace,et al.  Nitrogen fertilizer management for nitrous oxide (N2O) mitigation in intensive corn (Maize) production: an emissions reduction protocol for US Midwest agriculture , 2010 .

[27]  E. Pattey,et al.  Modeling the Effects of Fertilizer Application Rate on Nitrous Oxide Emissions , 2006 .

[28]  Philippe Ciais,et al.  New model for capturing the variations of fertilizer‐induced emission factors of N2O , 2015 .

[29]  E. Stehfest,et al.  N2O and NO emission from agricultural fields and soils under natural vegetation: summarizing available measurement data and modeling of global annual emissions , 2006, Nutrient Cycling in Agroecosystems.

[30]  W. J. Riley,et al.  Nitrogen leaching and soil nitrate, nitrite, and ammonium levels under irrigated wheat in Northern Mexico , 2001, Nutrient Cycling in Agroecosystems.

[31]  William R. Raun,et al.  PAPER PRESENTED AT INTERNATIONAL WORKSHOP ON INCREASING WHEAT YIELD POTENTIAL, CIMMYT, OBREGON, MEXICO, 20–24 MARCH 2006 Reduced nitrogen and improved farm income for irrigated spring wheat in the Yaqui Valley, Mexico, using sensor based nitrogen management , 2007, The Journal of Agricultural Science.

[32]  A. Mosier,et al.  Influence of elevated atmospheric carbon dioxide and supplementary irrigation on greenhouse gas emissions from a spring wheat crop in southern Australia , 2012, The Journal of Agricultural Science.

[33]  Peter Grace,et al.  Nonlinear nitrous oxide (N2O) response to nitrogen fertilizer in on‐farm corn crops of the US Midwest , 2011 .

[34]  G. Robertson Soil greenhouse gas emissions and their mitigation , 2014 .

[35]  E. Davidson,et al.  Managing nitrogen for sustainable development , 2015, Nature.

[36]  John A. Harrison,et al.  Escalating Worldwide use of Urea – A Global Change Contributing to Coastal Eutrophication , 2006 .

[37]  Kaicun Wang,et al.  Responses of N 2 O and CH 4 fluxes to fertilizer nitrogen addition rates in an irrigated wheat-maize cropping system in northern China , 2011 .

[38]  D. Murphy,et al.  Nitrous oxide emissions from a cropped soil in a semi‐arid climate , 2007 .

[39]  Pierre Friedlingstein,et al.  The terrestrial biosphere as a net source of greenhouse gases to the atmosphere , 2016, Nature.

[40]  Pamela A. Matson,et al.  Agricultural runoff fuels large phytoplankton blooms in vulnerable areas of the ocean , 2005, Nature.

[41]  N. Millar,et al.  N-related greenhouse gases in North America: innovations for a sustainable future , 2014 .

[42]  R. Gehl,et al.  In situ measurements of nitrate leaching implicate poor nitrogen and irrigation management on sandy soils. , 2005, Journal of environmental quality.