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RESEARCH ARTICLE

Strategies to mitigate greenhouse gas emissions in intensively managed vegetable cropping systems in subtropical Australia

M. Rezaei Rashti A B C E , W. J. Wang A B E , S. M. Harper D , P. W. Moody A , C. R. Chen B C , H. Ghadiri B C and S. H. Reeves A
+ Author Affiliations
- Author Affiliations

A Department of Science, Information Technology and Innovation (DSITI), Dutton Park, Qld 4102, Australia.

B Environmental Futures Research Institute, Griffith University, Nathan, Qld 4111, Australia.

C Griffith School of Environment, Griffith University, Nathan, Qld 4111, Australia.

D Department of Agriculture and Fisheries, Warrego Highway, Gatton, Qld 4343, Australia.

E Corresponding authors. Email: m.rezaeirashti@griffith.edu.au; weijin.wang@qld.gov.au

Soil Research 53(5) 475-484 https://doi.org/10.1071/SR14355
Submitted: 7 December 2014  Accepted: 17 March 2015   Published: 20 August 2015

Abstract

The greenhouse gas fluxes and effective mitigation strategies in subtropical vegetable cropping systems remain unclear. In this field experiment, nitrous oxide (N2O) and methane (CH4) fluxes from an irrigated lettuce cropping system in subtropical Queensland, Australia, were measured using manual sampling chambers. Four treatments were included: Control (no fertiliser), U100 (100 kg N ha–1 as urea), U200 (200 kg N ha–1 as urea) and N100 (100 kg N ha–1 as nitrate-based fertilisers). The N fertilisers were applied in three splits and irrigation was delivered sparingly and frequently to keep soil moisture around the field capacity. The cumulative N2O emissions from the control, U100, U200 and N100 treatments over the 68-day cropping season were 30, 151, 206 and 68 g N2O-N ha–1, respectively. Methane emission and uptake were negligible. Using N2O emission from the Control treatment as the background emission, direct emission factors for U100, U200 and N100 treatments were 0.12%, 0.09% and 0.04% of applied fertiliser N, respectively. Soil ammonium (NH4+) concentration, instead of nitrate (NO3) concentration, exhibited a significant correlation with N2O emissions at the site where the soil moisture was controlled within 50%–64% water-filled pore space. Furthermore, soil temperature rather than water content was the main regulating factor of N2O fluxes in the fertilised treatments. Fertiliser type and application rates had no significant effects on yield parameters. Partial N balance analysis indicated that approximately 80% and 52% of fertiliser N was recovered in plants and soil in the treatments receiving 100 kg N ha–1 and 200 kg N ha–1, respectively. Therefore, in combination with frequent and low-intensity irrigation and split application of fertiliser N, substitution of NO3-based fertilisers for urea and reduction in fertiliser N application rates were considered promising mitigation strategies to maintain yield and minimise N2O emissions during the low rainfall season.

Additional keywords: methane, nitrous oxide, subtropical climate, vegetable.


References

Ambus P, Christensen S (1995) Spatial and seasonal nitrous oxide and methane fluxes in Danish forest, grassland, and agroecosystems. Journal of Environmental Quality 24, 993–1001.
Spatial and seasonal nitrous oxide and methane fluxes in Danish forest, grassland, and agroecosystems.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2MXot1Wksb4%3D&md5=b78b7bb9f25cff014d41fd467b059c88CAS |

Ball BC, Smith KA, Klemedtsson L, Brumme R, Sitaula BK, Hansen S, Prieme A, MacDonald J, Horgan GW (1997) The influence of soil gas transport properties on methane oxidation in a selection of northern European soils. Journal of Geophysical Research 102, 23309–23317.
The influence of soil gas transport properties on methane oxidation in a selection of northern European soils.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2sXntVyltbs%3D&md5=6ebe29ab08813a884007a44dabd95984CAS |

Cassel DK, Nielsen DR (1986) Field capacity and available water capacity. In ‘Methods of soil analysis. Part 1: physical and mineralogical methods’. (Ed. A Klute) pp. 901–926. (American Society of Agronomy and Soil Science Society of America: Madison, WI, USA)

Dalal RC, Mayer RJ (1986) Long term trends in fertility of soils under continuous cultivation and cereal cropping in southern Queensland. I. Overall changes in soil properties and trends in winter cereal yields. Soil Research 24, 265–279.
Long term trends in fertility of soils under continuous cultivation and cereal cropping in southern Queensland. I. Overall changes in soil properties and trends in winter cereal yields.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaL28XkvFKmsL8%3D&md5=ff4db3af81bf05a7fdd15051160443fdCAS |

Dalal RC, Wang W, Robertson GP, Parton WJ (2003) Nitrous oxide emission from Australian agricultural lands and mitigation options: a review. Soil Research 41, 165–195.
Nitrous oxide emission from Australian agricultural lands and mitigation options: a review.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3sXktFKisr8%3D&md5=207b19866924d44a696cc4ace7867060CAS |

Davidson EA (1991) Fluxes of nitrous oxide and nitric oxide from terrestrial ecosystems. In ‘Microbial production and consumption of greenhouse gases: methane, nitrogen oxides and halomethanes’. (Eds JE Rogers, WB Whitman) pp. 219–235. (American Society of Microbiology: Washington, DC)

De Klein CAM, Van Logtestijn RSP (1996) Denitrification in grassland soils in The Netherlands in relation to irrigation, N-application rate, soil water content and soil temperature. Soil Biology & Biochemistry 28, 231–237.
Denitrification in grassland soils in The Netherlands in relation to irrigation, N-application rate, soil water content and soil temperature.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK28XhtlClurk%3D&md5=6d8abdf1dc5a5ece884d360175aad95aCAS |

Del Grosso SJ, Ojima DS, Parton WJ, Stehfest E, Heistemann M, DeAngelo B, Rose S (2009) Global scale DAYCENT model analysis of greenhouse gas emissions and mitigation strategies for cropped soils. Global and Planetary Change 67, 44–50.
Global scale DAYCENT model analysis of greenhouse gas emissions and mitigation strategies for cropped soils.Crossref | GoogleScholarGoogle Scholar |

Deng J, Zhou Z, Zheng X, Liu C, Yao Z, Xie B, Cui F, Han S, Zhu J (2012) Annual emissions of nitrous oxide and nitric oxide from rice–wheat rotation and vegetable fields: a case study in the Tai-Lake region, China. Plant and Soil 360, 37–53.
Annual emissions of nitrous oxide and nitric oxide from rice–wheat rotation and vegetable fields: a case study in the Tai-Lake region, China.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC38XhsFWisLfL&md5=128454477ac4ef299eb46c79a4534c9dCAS |

Diao T, Xie L, Guo L, Yan H, Lin M, Zhang H, Lin J, Lin E (2013) Measurements of N2O emissions from different vegetable fields on the North China Plain. Atmospheric Environment 72, 70–76.
Measurements of N2O emissions from different vegetable fields on the North China Plain.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3sXlsVKmsbk%3D&md5=30629370a2c5882109912a3c5d6381fbCAS |

Ding W, Cai Y, Cai Z, Yagi K, Zheng X (2007a) Nitrous oxide emissions from an intensively cultivated maize–wheat rotation soil in the North China Plain. The Science of the Total Environment 373, 501–511.
Nitrous oxide emissions from an intensively cultivated maize–wheat rotation soil in the North China Plain.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2sXhtlams7c%3D&md5=195c6f8b739ac18d524a2f923d8ae588CAS | 17229455PubMed |

Ding W, Meng L, Cai Z, Han F (2007b) Effects of long-term amendment of organic manure and nitrogen fertiliser on nitrous oxide emission in a sandy loam soil. Journal of Environmental Sciences 19, 185–193.
Effects of long-term amendment of organic manure and nitrogen fertiliser on nitrous oxide emission in a sandy loam soil.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2sXjt1SmtLk%3D&md5=ec70ab10b2257c8b0e125bdad0505799CAS |

Dobbie KE, Smith KA (1996) Comparison of CH4 oxidation rates in woodland, arable and set aside soils. Soil Biology & Biochemistry 28, 1357–1365.
Comparison of CH4 oxidation rates in woodland, arable and set aside soils.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2sXos1Sksw%3D%3D&md5=2272af71a0c146339ec61dfa7b6b26f5CAS |

Dobbie KE, Smith KA (2003) Nitrous oxide emission factors for agricultural soils in Great Britain: the impact of soil water-filled pore space and other controlling variables. Global Change Biology 9, 204–218.
Nitrous oxide emission factors for agricultural soils in Great Britain: the impact of soil water-filled pore space and other controlling variables.Crossref | GoogleScholarGoogle Scholar |

Dobbie KE, McTaggart IP, Smith KA (1999) Nitrous oxide emissions from intensive agricultural systems: variations between crops and seasons, key driving variables, and mean emission factors. Journal of Geophysical Research 104, 26 891–26 899.
Nitrous oxide emissions from intensive agricultural systems: variations between crops and seasons, key driving variables, and mean emission factors.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK1MXotFajsL0%3D&md5=1cfc00625aae5d9b199db37b6bbf29bdCAS |

Dong H, Zhu Z, Shang B, Kang G, Zhu H, Xin H (2007) Greenhouse gas emissions from swine barns of various production stages in suburban Beijing, China. Atmospheric Environment 41, 2391–2399.
Greenhouse gas emissions from swine barns of various production stages in suburban Beijing, China.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2sXitFSku7c%3D&md5=c22132282f2ff6b385e85d0ca2acf19eCAS |

FAOSTAT (2014) FAOSTAT agricultural data. Available at: http://faostat3.fao.org/faostatgateway/go/to/download/G1/GY/E (accessed 1 August 2014).

Gallardo M, Jackson LE, Thompson RB (1996) Shoot and root physiological responses to localized zones of soil moisture in cultivated and wild lettuce (Lactuca spp.). Plant, Cell & Environment 19, 1169–1178.
Shoot and root physiological responses to localized zones of soil moisture in cultivated and wild lettuce (Lactuca spp.).Crossref | GoogleScholarGoogle Scholar |

He F, Chen Q, Jiang R, Chen X, Zhang F (2007) Yield and nitrogen balance of greenhouse tomato (Lycopersicum esculentum Mill.) with conventional and site-specific nitrogen management in northern China. Nutrient Cycling in Agroecosystems 77, 1–14.
Yield and nitrogen balance of greenhouse tomato (Lycopersicum esculentum Mill.) with conventional and site-specific nitrogen management in northern China.Crossref | GoogleScholarGoogle Scholar |

He F, Jiang R, Chen Q, Zhang F, Su F (2009) Nitrous oxide emissions from an intensively managed greenhouse vegetable cropping system in Northern China. Environmental Pollution 157, 1666–1672.
Nitrous oxide emissions from an intensively managed greenhouse vegetable cropping system in Northern China.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1MXktF2ks7Y%3D&md5=bcf96f45a736ffdbe27c302d5b45d25eCAS | 19167792PubMed |

Huang B, Shi X, Yu D, Oborn I, Blombäck K, Pagella TF, Wang H, Sun W, Sinclair FL (2006) Environmental assessment of small-scale vegetable farming systems in peri-urban areas of the Yangtze River Delta Region, China. Agriculture, Ecosystems & Environment 112, 391–402.
Environmental assessment of small-scale vegetable farming systems in peri-urban areas of the Yangtze River Delta Region, China.Crossref | GoogleScholarGoogle Scholar |

IPCC (2006) ‘IPCC guidelines for national greenhouse gas inventories. Agriculture, forestry and other land use. Vol. 4.’ (IGES: Kanagawa, Japan)

IPCC 2013 ‘Climatic change 2013: the physical science basis.’ (Cambridge University Press: Cambridge, UK)

Isbell RF (2002) ‘The Australian soil classification.’ Revised edn. (CSIRO Publishing: Melbourne)

Jackson LE, Stivers LJ, Warden BT, Tanji KK (1994) Crop nitrogen utilization and soil nitrate loss in a lettuce field. Fertilizer Research 37, 93–105.
Crop nitrogen utilization and soil nitrate loss in a lettuce field.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2cXmtVChsLc%3D&md5=46e6f17b91d4e21037fd8ba9ce395bcaCAS |

Jia J, Sun L, Kong X, Yan X, Xiong Z (2012) Annual N2O and CH4 emissions from intensively managed vegetable fields in Nanjing, China. Soil Science and Plant Nutrition 58, 91–103.
Annual N2O and CH4 emissions from intensively managed vegetable fields in Nanjing, China.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC38XisFaru7g%3D&md5=aa9062f603ad04dac19940d00941df19CAS |

Kim D-G, Hernandez-Ramirez G, Giltrap D (2013) Linear and nonlinear dependency of direct nitrous oxide emissions on fertilizer nitrogen input: a meta-analysis. Agriculture, Ecosystems & Environment 168, 53–65.
Linear and nonlinear dependency of direct nitrous oxide emissions on fertilizer nitrogen input: a meta-analysis.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3sXltVyhs7k%3D&md5=8304bcc6a8cdb6988851be20ad472dedCAS |

Liu C, Zheng X, Zhou Z, Han S, Wang Y, Wang K, Liang W, Li M, Chen D, Yang Z (2010) Nitrous oxide and nitric oxide emissions from an irrigated cotton field in Northern China. Plant and Soil 332, 123–134.
Nitrous oxide and nitric oxide emissions from an irrigated cotton field in Northern China.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3cXntlGhurs%3D&md5=2b42e785dcec0bf01292b5b53c7c07b5CAS |

Ludwig J, Meixner FX, Vogel B, Förstner J (2001) Soil–air exchange of nitric oxide: an overview of processes, environmental factors, and modeling studies. Biogeochemistry 52, 225–257.
Soil–air exchange of nitric oxide: an overview of processes, environmental factors, and modeling studies.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3MXkt1Krsbk%3D&md5=5e8a0c8c8592088405c076fe3a1a94ecCAS |

Mosier A, Kroeze C (2000) Potential impact on the global atmospheric N2O budget of the increased nitrogen input required to meet future global food demands. Chemosphere. Global Change Science 2, 465–473.
Potential impact on the global atmospheric N2O budget of the increased nitrogen input required to meet future global food demands.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3cXos1egsLk%3D&md5=6612f820af08a5611026b0423953328eCAS |

Mosier AR, Duxbury JM, Freney JR, Heinemeyer O, Minami K, Johnson DE (1998) Mitigating agricultural emissions of methane. Climatic Change 40, 39–80.
Mitigating agricultural emissions of methane.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK1cXmslWgu70%3D&md5=046fca62ca092ecb0ec9d78edbe45df5CAS |

Patil S, Singh U, Singh V, Mishra V, Das R, Henao J (2001) Nitrogen dynamics and crop growth on an Alfisol and a Vertisol under a direct-seeded rainfed lowland rice-based system. Field Crops Research 70, 185–199.
Nitrogen dynamics and crop growth on an Alfisol and a Vertisol under a direct-seeded rainfed lowland rice-based system.Crossref | GoogleScholarGoogle Scholar |

Rayment GE, Lyons DJ (2011) ‘Soil chemical methods: Australasia.’ (CSIRO Publishing: Melbourne)

Ruser R, Schilling R, Steindl H, Flessa H, Beese F (1998) Soil compaction and fertilization effects on nitrous oxide and methane fluxes in potato fields. Soil Science Society of America Journal 62, 1587–1595.
Soil compaction and fertilization effects on nitrous oxide and methane fluxes in potato fields.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK1MXjslygtQ%3D%3D&md5=1c341ae70580dec8174f3088deeeff6cCAS |

Russow R, Sich I, Neue HU (2000) The formation of the trace gases NO and N2O in soils by the coupled processes of nitrification and denitrification: results of kinetic 15N tracer investigations. Chemosphere. Global Change Science 2, 359–366.
The formation of the trace gases NO and N2O in soils by the coupled processes of nitrification and denitrification: results of kinetic 15N tracer investigations.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3cXos1egs7g%3D&md5=a9f5390048d6a13db50492ed184914d1CAS |

Sehy U, Ruser R, Munch JC (2003) Nitrous oxide fluxes from maize fields: relationship to yield, site-specific fertilisation, and soil conditions. Agriculture, Ecosystems & Environment 99, 97–111.
Nitrous oxide fluxes from maize fields: relationship to yield, site-specific fertilisation, and soil conditions.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3sXnvVKrtbc%3D&md5=6227ed4942dca724f05fe2993fbf8f86CAS |

Shcherbak I, Millar N, Robertson GP (2014) Global metaanalysis of the nonlinear response of soil nitrous oxide (N2O) emissions to fertilizer nitrogen. Proceedings of the National Academy of Sciences of the United States of America 111, 9199–9204.

Smith P, Martino D, Cai Z, Gwary D, Janzen H, Kumar P, McCarl B, Ogle S, O’Mara F, Rice C, Scholes B, Sirotenko O, Howden M, McAllister T, Pan G, Romanenkov V, Schneider U, Towprayoon S, Wattenbach M, Smith J (2008) Greenhouse gas mitigation in agriculture. Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences 363, 789–813.
Greenhouse gas mitigation in agriculture.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXislGgtb8%3D&md5=38ee6ac73713fb22d91d88d361363f24CAS | 17827109PubMed |

Striegl RG (1993) Diffusional limits to the consumption of atmospheric methane by soils. Chemosphere 26, 715–720.
Diffusional limits to the consumption of atmospheric methane by soils.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK3sXitFyksrk%3D&md5=459597b06bbe7293ab10421af14b18dcCAS |

Tan IYS, van Es HM, Duxbury JM, Melkonian JJ, Schindelbeck RR, Geohring LD, Hively WD, Moebius BN (2009) Single-event nitrous oxide losses under maize production as affected by soil type, tillage, rotation, and fertilization. Soil & Tillage Research 102, 19–26.
Single-event nitrous oxide losses under maize production as affected by soil type, tillage, rotation, and fertilization.Crossref | GoogleScholarGoogle Scholar |

Thornton FC, Shurpali NJ, Bock BR, Reddy KC (1998) N2O and no emissions from poultry litter and urea applications to Bermuda grass. Atmospheric Environment 32, 1623–1630.
N2O and no emissions from poultry litter and urea applications to Bermuda grass.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK1cXjt1Grsrc%3D&md5=108d1b4f3461df68770a1350ef6490dbCAS |

Vallejo A, Garcia-Torres L, Diez JA, Arce A, Lopez-Fernandez S (2005) Comparison of N losses (NO3 –, N2O, NO) from surface applied, injected or amended (DCD) pig slurry of an irrigated soil in a Mediterranean climate. Plant and Soil 272, 313–325.
Comparison of N losses (NO3 , N2O, NO) from surface applied, injected or amended (DCD) pig slurry of an irrigated soil in a Mediterranean climate.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2MXks1ersr0%3D&md5=da6ed8de28fb82c35a9b4287cf91e358CAS |

Vanlauwe B, Wendt J, Diels J (2001) Combined application of organic matter and fertiliser. In ‘Sustaining soil fertility in West Africa’. (Eds G Tian, F Ishida, JDH Keatinge) pp. 247–279. (Soil Science Society of America and American Society of Agronomy: Madison, WI)

Vilain G, Garnier J, Tallec G, Cellier P (2010) Effect of slope position and land use on nitrous oxide (N2O) emissions (Seine Basin, France). Agricultural and Forest Meteorology 150, 1192–1202.
Effect of slope position and land use on nitrous oxide (N2O) emissions (Seine Basin, France).Crossref | GoogleScholarGoogle Scholar |

Wagner-Riddle C, Furon A, McLaughlin NL, Lee I, Barbeau J, Jayasundara S, Parkin G, Von Bertoldi P, Warland JON (2007) Intensive measurement of nitrous oxide emissions from a corn–soybean–wheat rotation under two contrasting management systems over 5 years. Global Change Biology 13, 1722–1736.
Intensive measurement of nitrous oxide emissions from a corn–soybean–wheat rotation under two contrasting management systems over 5 years.Crossref | GoogleScholarGoogle Scholar |

Wang WJ, Dalal RC, Reeves SH, Butterbach-Bahl K, Kiese R (2011) Greenhouse gas fluxes from an Australian subtropical cropland under long-term contrasting management regimes. Global Change Biology 17, 3089–3101.
Greenhouse gas fluxes from an Australian subtropical cropland under long-term contrasting management regimes.Crossref | GoogleScholarGoogle Scholar |

Xiong Z, Xie Y, Xing G, Zhu Z, Butenhoff C (2006) Measurements of nitrous oxide emissions from vegetable production in China. Atmospheric Environment 40, 2225–2234.
Measurements of nitrous oxide emissions from vegetable production in China.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD28XhsFGksro%3D&md5=b4a8373ffe3b669be57705a755b805f6CAS |

Yan X, Akimoto H, Ohara T (2003) Estimation of nitrous oxide, nitric oxide and ammonia emissions from croplands in East, Southeast and South Asia. Global Change Biology 9, 1080–1096.
Estimation of nitrous oxide, nitric oxide and ammonia emissions from croplands in East, Southeast and South Asia.Crossref | GoogleScholarGoogle Scholar |