Emissions of methane and nitrous oxide from Australian sugarcane soils.

Abstract Climatic conditions and cultural practices in the sub-tropical and tropical high-rainfall regions in which sugarcane is grown in Australia are conducive to rapid carbon and nitrogen cycling. Previous research has identified substantial exchanges of methane (CH 4 ) and nitrous oxide (N 2 O) between sugarcane soils and the atmosphere. However, that research has been mostly short-term. This paper describes recent work aimed at quantifying exchanges of CH 4 and N 2 O from fertilised sugarcane soils over whole growing seasons. Micrometeorological and chamber techniques provided continuous measurements of gas emissions in whole-of-season studies in a burnt-cane crop on an acid sulfate soil (ASS) that was fertilised with 160 kg nitrogen (N) ha −1 as urea in the south of the sugarcane belt (Site 1), and in a crop on a more representative trash-blanketed soil fertilised with 150 kg urea-N ha −1 in the north (Site 2). Site 1 was a strong source of CH 4 with a seasonal emission (over 342 days) of 19.9 kg CH 4  ha −1 . That rate corresponds to 0.5–5% of those expected from rice and wetlands. The many drains in the region appear to be the main source. The net annual emission of CH 4 at Site 2 over 292 days was essentially zero, which contradicts predictions that trash-blankets on the soil are net CH 4 sinks. Emissions of N 2 O from the ASS at Site 1 were extraordinarily large and prolonged, totalling 72.1 kg N 2 O ha −1 (45.9 kg N ha −1 ) and persisting at substantial rates for 5 months. The high porosity and frequent wetting with consequent high water filled pore space and the high carbon content of the soil appear to be important drivers of N 2 O production. At Site 2, emissions were much smaller, totalling 7.4 kg N 2 O ha −1 (4.7 kg N ha −1 ), most of which was emitted in less than 3 months. The emission factors for N 2 O (the proportion of fertiliser nitrogen emitted as N 2 O–N) were 21% at Site 1 and 2.8% at Site 2. Both factors exceed the default national inventory value of 1.25%. Calculations suggest that annual N 2 O production from Australian sugarcane soils is around 3.8 kt N 2 O, which is about one-half a previous estimate based on short-term measurements, and although ASS constitute only about 4% of Australia's sugarcane soils, they could contribute about 25% of soil emissions of N 2 O from sugarcane. The uptake of 50–94 t CO 2  ha −1 from the atmosphere by the crops at both sites was offset by emissions of CH 4 and N 2 O to the atmosphere amounting to 22 t CO 2 -e ha −1 at Site 1 and 2 t CO 2 -e ha −1 at Site 2.

[1]  H. Neue,et al.  Methane Emissions from Major Rice Ecosystems in Asia , 2012, Developments in Plant and Soil Sciences.

[2]  O. T. Denmead,et al.  Approaches to measuring fluxes of methane and nitrous oxide between landscapes and the atmosphere , 2008, Plant and Soil.

[3]  Michael R. Raupach,et al.  Simplified expressions for vegetation roughness length and zero-plane displacement as functions of canopy height and area index , 1994 .

[4]  John H. Prueger,et al.  Turbulent Schmidt number from a tracer experiment , 2002 .

[5]  W. Parton,et al.  Nitrous oxide emission from Australian agricultural lands and mitigation options: a review , 2003 .

[6]  D. M. Hogarth,et al.  Sugarcane : research towards efficient and sustainable production , 1996 .

[7]  I. White,et al.  Floodplain hydrology, acid discharge and change in water quality associated with a drained acid sulfate soil , 1999 .

[8]  K. Weier N2O and CH4 emission and CH4 consumption in a sugarcane soil after variation in nitrogen and water application , 1999 .

[9]  K. Mcnaughton On the Kinetic Energy Budget of the Unstable Atmospheric Surface Layer , 2006 .

[10]  John M. Melack,et al.  Methane flux from the central Amazonian floodplain , 1988 .

[11]  J. Finnigan,et al.  Atmospheric Boundary Layer Flows: Their Structure and Measurement , 1994 .

[12]  Ian White,et al.  Whole-of-season greenhouse gas emissions from Australian Sugarcane soils , 2008 .

[13]  R. Harriss,et al.  Biogenic trace gases : measuring emissions from soil and water , 1995 .

[14]  E. K. Webb Profile relationships: The log‐linear range, and extension to strong stability , 1970 .

[15]  K. Butterbach‐Bahl,et al.  N2O emission from tropical forest soils of Australia , 2000 .

[16]  D. Griffith Synthetic Calibration and Quantitative Analysis of Gas-Phase FT-IR Spectra , 1996 .

[17]  Ward N. Smith,et al.  Tools for quantifying N2O emissions from agroecosystems , 2007 .

[18]  B. Hicks,et al.  Flux‐gradient relationships in the constant flux layer , 1970 .

[19]  Jerry L. Hatfield,et al.  Micrometeorology in Agricultural Systems , 2005 .

[20]  Corinne Le Quéré,et al.  Climate Change 2013: The Physical Science Basis , 2013 .

[21]  William P. Kustas,et al.  Aerodynamic Methods for Estimating Turbulent Fluxes , 2005 .

[22]  D. Baldocchi Assessing the eddy covariance technique for evaluating carbon dioxide exchange rates of ecosystems: past, present and future , 2003 .

[23]  R. Leuning,et al.  A study of environmental and management drivers of non-CO2 greenhouse gas emissions in Australian agro-ecosystems , 2005 .

[24]  R. Dalal,et al.  GREENHOUSE GAS EMISSIONS FROM SUGARCANE SOILS AND NITROGEN FERTILISER MANAGEMENT: II By , 2006 .

[25]  D. Griffith,et al.  Acid sulfate soils: a new source of sulfur and greenhouse gases. , 2005 .

[26]  C. Paulson The Mathematical Representation of Wind Speed and Temperature Profiles in the Unstable Atmospheric Surface Layer , 1970 .

[27]  E. K. Webb,et al.  Correction of flux measurements for density effects due to heat and water vapour transfer , 1980 .

[28]  K. Weier Trace gas emissions from a trash blanketed sugarcane field in tropical Australia , 1996 .

[29]  J. Ehrenfeld,et al.  Ammonium oxidation coupled to dissimilatory reduction of iron under anaerobic conditions in wetland soils , 2005 .

[30]  Anònim Anònim Keys to Soil Taxonomy , 2010 .

[31]  K. Weier Sugarcane fields: sources or sinks for greenhouse gas emissions? , 1998 .

[32]  J. I. MacPherson,et al.  Application of a tunable diode laser to the measurement of CH4 and N2O fluxes from field to landscape scale using several micrometeorological techniques , 2006 .

[33]  R. Betts,et al.  Changes in Atmospheric Constituents and in Radiative Forcing. Chapter 2 , 2007 .

[34]  F. Kelliher,et al.  Measuring methane emission rates of a dairy cow herd by two micrometeorological techniques , 2004 .

[35]  I. Vallis,et al.  Potential for biological denitrification of fertilizer nitrogen in sugarcane soils , 1996 .

[36]  Ray Leuning,et al.  Nitrous oxide flux measurements from an intensively managed irrigated pasture using micrometeorological techniques , 2007 .

[37]  D. Griffith,et al.  Air-land exchanges of CO2, CH4 and N2O measured by FTIR spectrometry and micrometeorological techniques , 2002 .

[38]  R. Dalal,et al.  NITROUS OXIDE EMISSIONS FROM SUGARCANE SOILS: EFFECTS OF UREA FORMS AND APPLICATION RATE , 2008 .