Rodney Venterea – USDA-ARS, Minnesota

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Presentation transcript:

Rodney Venterea – USDA-ARS, Minnesota Integrated Nutrient Management Network Rodney Venterea – USDA-ARS, Minnesota Mission:  Facilitate collaboration / communication among scientists and stakeholders around the role of nutrient management in decreasing the GHG footprint of agricultural production, and develop a knowledge base to improve use efficiency of fertilizer inputs. Volunteering Members: 20 individuals from 10 countries: AUSTRALIA, CANADA, CHINA, DENMARK, ETHIOPIA, FRANCE, JAPAN, NEW ZEALAND, SWEDEN, USA

Integrated Nutrient Management Network AUSTRALIA Peter Grace. Queensland University of Technology, Brisbane CANADA Martin Chantigny. Agriculture and Agri-Food Canada, Hochelaga, Québec Craig Drury. Agriculture and Agri-Food Canada, Harrow, Ontario Richard Farrell. University of Saskatchewan, Saskatoon, Saskatchewan Amanda Giamberardino. Fertilizer Canada, Ottawa, Ontario Mario Tenuta. University of Manitoba, Winnipeg, Manitoba CHINA Xiaotang Ju. China Agricultural University, Beijing Zhisheng Yao. Institute of Atmospheric Physics, Chinese Academy of Sciences, Beijing DENMARK Jørgen E. Olesen. Aarhus University, Aarhus ETHIOPIA Dong-Gill Kim. Hawassa University, Shashemenē

Integrated Nutrient Management Network FRANCE Pierre Cellier. INRA UMR INRA / AgroParisTech ECOSYS, Grignon JAPAN Ayaka W. Kishimoto. National Institute for Agro-Environmental Science, Tsukuba NEW ZEALAND Timothy Clough. Lincoln University, Canterbury SWEDEN Thomas Kätterer. Swedish University of Agricultural Sciences, Uppsala USA Michel Cavigelli. USDA-ARS, Beltsville MD Chuck Rice. Kansas State University Upendra Sainju. USDA-ARS, Sidney, MT Clifford S. Snyder. International Plant Nutrition Institute David Tarkalson. USDA-ARS, Kimberly, ID Rodney Venterea. USDA-ARS, Saint Paul, MN

GHG Mitigation Summary / Fact sheet under development: (a product but also as a means of generating discussion) Goal/Question: How can improved nutrient management assist in mitigation of greenhouse gas emissions from croplands? What is the issue? What are the factors controlling responses? What are expected responses? How can research help in refining mitigation estimates? Synthesis / recommendations

What are the issues? The availability of N limits crop productivity but application of N as fertilizers, manures, composts stimulates emission of N2O directly from the field. N application also generates other forms of reactive N (NH3, NO and NO3) which can be converted to N2O once released into the environment (indirect N2O). Nutrient application may also affect the release of CH4 and CO2 And other nutrients (P, S, etc) may affect any of the GHGs. Effective practices tend to vary by region and site, and depend on crop, soil, climate and other management factors. Summarizing this variability in a concise document will be a challenge – likely will focus on commonalities and important regional differences Meta-analyses that account for regional differences would be ideal

What are the factors controlling responses? Management factors 4Rs -Rate of N applied -Chemical form of synthetic fertilizers; manure source; coated fertilizers and/or microbial inhibitors -Timing of application (fall vs spring, preplant v sidedress) -Placement method (surface vs. incorporation, broadcast vs. banding) -Other practices: amendments (biochar), tillage, water, residue, plastic mulching Soil factors Texture, structure, drainage characteristics, organic matter content, bulk density, pH, soil biology (microbial community, earthworms)   Climate factors Precipitation amounts and seasonal patterns, temperature, aridity index Episodic climate events such as rewetting of dry soil; thawing of frozen soils

What are expected responses? Direct and/or indirect N2O emissions tend to decrease with: -Reduced rate of N input – by amount that does not impact yield -N rate reduction combined with other practices (inhibitors, improved timing) -N application later in the season, esp when combined with nitrification inhibitors -Use of urea instead of anhydrous ammonia, or NO3- instead of NH4 based sources -Coated fertilizers, but may be more reliable in irrigated systems

How can research help in refining mitigation estimates? -Need to define practices that are effective and quantify mitigation rates by region, cropping system, soil type, etc expressed as % reduction and/or using EFs -To quantify reductions both on an area and yield-scaled basis -To quantify indirect N2O emissions which are more uncertain that direct estimates; recent measurements suggesting N2O from NO3- in aquatic systems higher than EFs -Fill in gaps for emerging practices with limited or conflicting data, e.g. Precision agriculture (variable rate) Biochar Cover crops, living mulch systems Different types of microbial inhibitors Defining best application methods and rates for the inhibitors

How can research help in refining mitigation estimates? Trade-offs between direct and indirect N2O emissions: -Banding fertilizers or manures can decrease NH3 emissions but increase direct N2O -Use of nitrification inhibitors together with banding may be solution Xiaotang Ju. China Agricultural University, Beijing

How can research help in refining mitigation estimates? “There is a great gap in the South causing many problems in current efforts to mitigate GHG emissions - current mitigation research is driven by advanced technology. There is a need for collaborations North-South and South-South collaborations to identify and develop appropriate strategies with medium level of technology and with low cost, which the South can utilize and produce.”   Dong-Gill Kim. Hawassa University, Shashemenē, Ethiopia

Synthesis / Recommendations Work in progress Awaiting input from members