Challenges of accounting nitrous oxide emissions from agricultural crop residues

Author:

Olesen Jørgen E.1ORCID,Rees Robert M.2ORCID,Recous Sylvie3ORCID,Bleken Marina A.4ORCID,Abalos Diego1ORCID,Ahuja Ishita56ORCID,Butterbach‐Bahl Klaus17ORCID,Carozzi Marco8ORCID,De Notaris Chiara19ORCID,Ernfors Maria10,Haas Edwin7ORCID,Hansen Sissel5ORCID,Janz Baldur7ORCID,Lashermes Gwenaëlle3ORCID,Massad Raia S.8ORCID,Petersen Søren O.1ORCID,Rittl Tatiana F.45ORCID,Scheer Clemens7ORCID,Smith Kate E.11ORCID,Thiébeau Pascal3ORCID,Taghizadeh‐Toosi Arezoo11213ORCID,Thorman Rachel E.11ORCID,Topp Cairistiona F. E.2ORCID

Affiliation:

1. Department of Agroecology, iCLIMATE, Land‐CRAFT Aarhus University Tjele Denmark

2. Scotland's Rural College Edinburgh UK

3. INRAE, FARE UMR, Université de Reims Champagne Ardenne Reims France

4. Faculty of Environmental Sciences and Natural Resource Management Norwegian University of Life Sciences Ås Norway

5. NORSØK‐Norwegian Centre for Organic Agriculture Tingvoll Norway

6. Norwegian Institute of Bioeconomy Research (NIBIO) Steinkjer Norway

7. Institute of Meteorology and Climate Research (IMK‐IFU) Karlsruhe Institute of Technology Garmisch‐Partenkirchen Germany

8. INRAE, AgroParisTech, UMR ECOSYS Université Paris‐Saclay Palaiseau France

9. Impacts on Agriculture, Forests and Ecosystem Services Division Euro‐Mediterranean Center on Climate Change Viterbo Italy

10. Department of Biosystems and Technology Swedish University of Agricultural Sciences Alnarp Sweden

11. ADAS Boxworth Cambridge UK

12. Danish Technological Institute Aarhus N Denmark

13. Centre for Ecology & Hydrology Lancaster Environment Centre Lancaster UK

Abstract

AbstractCrop residues are important inputs of carbon (C) and nitrogen (N) to soils and thus directly and indirectly affect nitrous oxide (N2O) emissions. As the current inventory methodology considers N inputs by crop residues as the sole determining factor for N2O emissions, it fails to consider other underlying factors and processes. There is compelling evidence that emissions vary greatly between residues with different biochemical and physical characteristics, with the concentrations of mineralizable N and decomposable C in the residue biomass both enhancing the soil N2O production potential. High concentrations of these components are associated with immature residues (e.g., cover crops, grass, legumes, and vegetables) as opposed to mature residues (e.g., straw). A more accurate estimation of the short‐term (months) effects of the crop residues on N2O could involve distinguishing mature and immature crop residues with distinctly different emission factors. The medium‐term (years) and long‐term (decades) effects relate to the effects of residue management on soil N fertility and soil physical and chemical properties, considering that these are affected by local climatic and soil conditions as well as land use and management. More targeted mitigation efforts for N2O emissions, after addition of crop residues to the soil, are urgently needed and require an improved methodology for emission accounting. This work needs to be underpinned by research to (1) develop and validate N2O emission factors for mature and immature crop residues, (2) assess emissions from belowground residues of terminated crops, (3) improve activity data on management of different residue types, in particular immature residues, and (4) evaluate long‐term effects of residue addition on N2O emissions.

Funder

Agence Nationale de la Recherche

Bundesministerium für Ernährung und Landwirtschaft

Horizon 2020 Framework Programme

Innovationsfonden

Norges Forskningsråd

Publisher

Wiley

Subject

General Environmental Science,Ecology,Environmental Chemistry,Global and Planetary Change

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