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Biogeochemistry

, Volume 115, Issue 1–3, pp 317–332 | Cite as

A record of N2O and CH4 emissions and underlying soil processes of Korean rice paddies as affected by different water management practices

  • Sina Berger
  • Inyoung Jang
  • Juyoung Seo
  • Hojeong Kang
  • Gerhard Gebauer
Article

Abstract

Rice is staple food of half of mankind and paddy soils account for the largest anthropogenic wetlands on earth. Ample of research is being done to find cultivation methods under which the integrative greenhouse effect caused by emitted CH4 and N2O would be mitigated. Whereas most of the research focuses on quantifying such emissions, there is a lack of studies on the biogeochemistry of paddy soils. In order to deepen our mechanistic understanding of N2O and CH4 fluxes in rice paddies, we also determined NO3 and N2O concentrations as well as N2O isotope abundances and presence of O2 along soil profiles of paddies which underwent three different water managements during the rice growing season(s) in (2010 and) 2011 in Korea. Largest amounts of N2O (2 mmol m−2) and CH4 (14.5 mol m−2) degassed from the continuously flooded paddy, while paddies with less flooding showed 30–60 % less CH4 emissions and very low to negative N2O balances. In accordance, the global warming potential (GWP) was lowest for the Intermittent Irrigation paddy and highest for the Traditional Irrigation paddy. The N2O emissions could the best be explained (*P < 0.05) with the δ15N values and N2O concentrations in 40–50 cm soil depth, implying that major N2O production/consumption occurs there. No significant effect of NO3 on N2O production has been found. Our study gives insight into the soil of a rice paddy and reveals areas along the soil profile where N2O is being produced. Thereby it contributes to our understanding of subsoil processes of paddy soils.

Keywords

Nitrous oxide 15NO3 Traditional irrigation Intermittent irrigation Korea 

Notes

Acknowledgments

This work is part of the research group “Complex TERRain and ECOlogical Heterogeneity (TERRECO)” and financially supported by the German Research Foundation (DFG). We truly thank Heera Lee, Youngsun Kim and Bora Lee for the great language help. We thank Andreas Kolb, who constructed the portable vacuum pump for us and Isolde Baumann for skilful assistance by measuring N2O isotope abundances. We furthermore acknowledge Sebastian Arnholds help with digging and interpreting soil profiles and we are very thankful to John Tenhunen, who professionally coordinated the TERRECO fieldwork.

References

  1. Arth I, Frenzel P, Conrad R (1998) Denitrification coupled to nitrification in the rhizosphere of rice. Soil Biol Biochem 30:509–515CrossRefGoogle Scholar
  2. Bouwman AF, Boumans LJM, Batjes NH (2002) Modeling global annual N2O and NO emissions from fertilized fields. Glob Biogeochem Cycle 16:1080–1088Google Scholar
  3. Brand WA (1995) PreCon: a fully automated interface for the pre-GC concentration of trace gases in air for isotopic analyses. Isotopes Environ Health Stud 31:277–284CrossRefGoogle Scholar
  4. Cai ZC, Xing GX, Yan XY, Xu H, Tsuruta H, Yagi K, Minami K (1997) Methane and nitrous oxide emissions from rice paddy fields as affected by nitrogen fertilisers and water management. Plant Soil 196(1):7–14CrossRefGoogle Scholar
  5. Cai ZC, Laughlin RJ, Stevens RJ (2001) Nitrous oxide and dinitrogen emissions from soil under different water regimes and straw amendment. Chemosphere 42(2):113–121CrossRefGoogle Scholar
  6. Cao ZH, DeDatta SK, Fillery IRP (1984a) Effect of placement methods on floodwater properties and recovery of applied nitrogen 15 N labeled urea in wetland rice. Soil Sci Soc Am J 48:196–203CrossRefGoogle Scholar
  7. Cao ZH, DeDatta SK, Fillery IRP (1984b) N-15 balance and residual effects of urea-N in wetland rice fields as affected by deep placement techniques. Soil Sci Soc Am J 48:203–208CrossRefGoogle Scholar
  8. Cao JL, Ren LQ, Yang BL, Xu H, Xing GX, Zhang HK (1999) Characteristics of N2O emission from rice fields in a hilly area of southern Jiangsu province. Chin J Ecol 18:6–9 (In Chinese)Google Scholar
  9. Chapagain T, Yamaji E (2010) The effects of irrigation method, age of seedling and spacing on crop performance, productivity and water-wise rice production in Japan. Paddy Water Environ 8(1):81–90CrossRefGoogle Scholar
  10. Clayton H, McTaggart IP, Parker J, Swan L, Smith KA (1997) Nitrous oxide emissions from fertilized grassland: a 2-year study of the effects of N fertilizer form and environmental conditions. Biol Fertil Soils 25:252–260CrossRefGoogle Scholar
  11. DeDatta SK (1981) Principles and practices of rice production. Wiley, New YorkGoogle Scholar
  12. Dowrick DJ, Hughes S, Freeman C, Lock MA, Reynolds B, Hudson JA (1999) Nitrous oxide emissions from a gully mire in mid-Wales UK, under simulated summer drought. Biogeochemistry 44:151–162Google Scholar
  13. FAO (2006) Guidelines for soil description, 4th edn. Publishing Management Service, Information Division, FAO, RomeGoogle Scholar
  14. Ferré C, Zechmeister-Boltenstern S, Comolli R, Andersson M, Seufert G (2012) Soil microbial community structure in a rice paddy field and its relationships to CH4 and N2O fluxes. Nutr Cycl Agroecosyst 93:35–50CrossRefGoogle Scholar
  15. Freeman C, Lock MA, Hughes S, Reynolds B (1997) Nitrous oxide emissions and the use of wetlands for water quality amelioration. Environ Sci Technol 31:2438–2440CrossRefGoogle Scholar
  16. Frenzel P, Rothfuss F, Conrad R (1992) Oxygen profiles and methane turnover in a flooded rice microcosm. Biol Fertil Soils 14:84–89CrossRefGoogle Scholar
  17. Frolking S, Qiu J, Boles S, Xiao X, Liu J, Zhuang Y, Li C, Qin X (2002) Combining remote sensing and ground census data to develop new maps of the distribution of rice agriculture in China. Glob Biogeochem Cycle 16(4):1091–1101CrossRefGoogle Scholar
  18. Goldberg SD, Knorr K-H, Gebauer G (2008a) N2O concentration and isotope signature along profiles provide deeper insight into the fate of N2O in soils. Isotopes Environ Health Stud 44:377–391CrossRefGoogle Scholar
  19. Goldberg SD, Muhr J, Borken W, Gebauer G (2008b) Fluxes of climate-relevant trace gases between a Norway spruce forest soil and atmosphere during repeated freeze-thaw cycles in mesocosms. J Soil Sci Plant Nutr 171:729–739CrossRefGoogle Scholar
  20. Goldberg SD, Knorr K-H, Blodau C, Lischeid G, Gebauer G (2010) Impact of altering the water table height of an acidic fen on N2O and NO fluxes and soil concentrations. Glob Change Biol 16:220–233CrossRefGoogle Scholar
  21. Granli T, Bøckman OC (1994) Nitrous oxide from agriculture. Norwegian J Agri Sci. Suppl. No. 12Google Scholar
  22. IPCC (2001) Radiative forcing of climate change. In: Houghton JT, Ding Y, Griggs DJ, Noguer M, van der Linden PJ, Dai X, Maskell K, Johnson CA (eds) Climate Change 2001: the scientific basis. Contribution of working group I to the third assessment report of the intergovernmental panel on climate change. Cambridge University Press, CambridgeGoogle Scholar
  23. IPCC (Intergovernmental Panel on Climate Change) (1992) The supplementary report to IPCC scientific assessment [Houghton JT, Callander BA, Varney SK (Eds)]. Cambridge University Press, CambridgeGoogle Scholar
  24. IUSS Working Group WRB (2007) World reference base for soil resources 2006 first update 2007. World Soil Resources Reports No. 103. FAO, RomeGoogle Scholar
  25. Johnson-Beebout SE, Angeles OR, Alberto MCR, Buresh RJ (2009) Simultaneous minimization of nitrous oxide and methane emission from rice paddy soils is improbable due to redox potential changes with depth in a greenhouse experiment without plants. Geoderma 149:45–53CrossRefGoogle Scholar
  26. Katoh M, Murase J, Hayashi M, Matsuya K, Kimura M (2004) Nutrient leaching from the plow layer by water percolation and accumulation in the subsoil in an irrigated paddy field. J Soil Sci Plant Nutr 50:721–729Google Scholar
  27. Khalil MI, Baggs EM (2005) CH4 oxidation and N2O emissions at varied soil water-filled pore spaces and headspace CH4 concentrations. Soil Biol Biochem 37(10):1785–1794CrossRefGoogle Scholar
  28. Klüber HD, Conrad R (1998) Effects of nitrate nitrite, NO and N2O on methanogenesis and other redox processes in anoxic rice field soil. FEMS Microbiol Ecol 25:301–318CrossRefGoogle Scholar
  29. Kögel-Knabner I, Amelung W, Cao Z, Fiedler S, Frenzel P, Jahn R, Kalbitz K, Kölbl A, Schloter M (2010) Biogeochemistry of paddy soils. Geoderma 157:1–14CrossRefGoogle Scholar
  30. Kool DM, Dolfing J, Wrage N, van Groenigen JW (2011) Nitrifier denitrification as a distinct and significant source of nitrous oxide from soil. Soil Biol Biochem 43:174–178CrossRefGoogle Scholar
  31. Li X, Yuan W, Xu H, Cai Z, Yagi K (2011) Effect of timing and duration of midseason aeration on CH4 and N2O emissions from irrigated lowland rice paddies in China. Nutr Cycl Agroecosyst 91:293–305CrossRefGoogle Scholar
  32. Liu SW, Qin YM, Zou JW, Liu QH (2010) Effects of water regime during rice-growing season on annual direct N2O emission in a paddy rice-winter wheat rotation system in southeast China. Sci Total Environ 408(4):906–913CrossRefGoogle Scholar
  33. Ma HL, Zhu JG, Xie ZB, Liu G, Zeng Q, Han Y (2007) Responses of rice and winter wheat to free-air CO2 enrichment (China FACE) at rice/wheat rotation system. Plant Soil 294:137–146CrossRefGoogle Scholar
  34. Maie N, Watanabe A, Kimura M (2004) Chemical characteristics and potential source of fulvic acids leached from the plow layer of paddy soil. Geoderma 120:309–323Google Scholar
  35. Mao Z (2002) Water saving irrigation for rice and its effect on environment. Eng Sci 4(7):8–16 (in Chinese)Google Scholar
  36. Mariotti A (1983) Atmospheric nitrogen is a reliable standard for natural δ15N abundance measurements. Nature 303:685–687CrossRefGoogle Scholar
  37. Martikainen PJ, Nykänen H, Crill P, Silvola J (1993) Effect of lowered water table on nitrous oxide emissions from northern peatlands. Nature 366:51–53CrossRefGoogle Scholar
  38. Michalzik B, Kalbitz K, Park JH, Solinger S, Matzner E (2001) Fluxes and concentrations of dissolved organic carbon and nitrogen—a synthesis for temperate forests. Biogeochem 52:173–205Google Scholar
  39. Miyazato T, Mohammed RA, Lazaro RC (2010) Irrigation management transfer (IMT) and system of rice intensification (SRI) practice in the Philippines. Paddy Water Environ 8:91–97CrossRefGoogle Scholar
  40. Neue H-U, Sass RL (1998) The budget of methane from rice fields. IGACtivities Newsletter 12:3–11Google Scholar
  41. Peng S, Hou H, Xu J, Mao Z, Abudu S, Luo Y (2011) Nitrous oxide emissions from paddy fields under different water managements in southeast China. Paddy Water Environ 9:403–411CrossRefGoogle Scholar
  42. Potter CS, Matson PA, Vitousek PM, Davidson EA (1996) Process modeling of controls on nitrogen trace gas emissions from soils worldwide. J Geophys Res 101:1361–1377CrossRefGoogle Scholar
  43. Qin Y, Liu S, Guo Y, Liu Q, Zou J (2010) Methane and nitrous oxide emissions from organic and conventional rice cropping systems in southeast China. Biol Fertil Soils 46:825–834CrossRefGoogle Scholar
  44. Reiche M, Torburg G, Küsel K (2007) Competition of Fe(III) reduction and methanogenesis in an acidic fen. FEMS Microbial Ecol 65:88–101CrossRefGoogle Scholar
  45. Robertson GP, Grace PR (2004) Greenhouse gas fluxes in tropical and temperate agriculture: the need for a full-cost accounting of global warming potentials. Environ Dev Sustain 6:51–63CrossRefGoogle Scholar
  46. Roy RN, Misra RV (2003) Economic and environmental impact of improved nitrogen management in Asian rice-farming systems. In: Proceedings of the 20th session of the international rice commission, Bangkok, Thailand, 23–26 July 2002. FAO, RomGoogle Scholar
  47. Sato S, Yamaji E, Kuroda T (2011) Strategies and engineering adaptations to disseminate SRI methods in large-scale irrigation systems in Eastern Indonesia. Paddy Water Environ 9:79–88CrossRefGoogle Scholar
  48. Seo J, Kang H (2012) Abundance of methanogens, methanotrophic bacteria, and denitrifiers in rice paddy soils (Unpublished manuscript)Google Scholar
  49. Sey B, Manceur A, Whalen J, Gregorich E, Rochette P (2008) Smallscale heterogeneity in carbon dioxide, nitrous oxide and methane production from aggregates of a cultivated sandy-loam soil. Soil Biol Biochem 40:2468–2473CrossRefGoogle Scholar
  50. Shepherd MF, Barzetti S, Hastie DR (1991) The production of atmospheric NOX and N2O from a fertilized agricultural soil. Atmos Environ 25A:1961–1969Google Scholar
  51. Smith CJ, Patrick WH (1983) Nitrous oxide emission as affected by alternate anaerobic and aerobic conditions from soil suspensions enriched with ammonium sulfate. Soil Biol Biochem 15:693–697CrossRefGoogle Scholar
  52. Tilsner J, Wrage N, Lauf J, Gebauer G (2003) Emission of gaseous nitrogen oxides from an extensively managed grassland in NE Bavaria, Germany. I. Annual budgets of N2O and NOx emissions. Biogeochemistry 63:229–247CrossRefGoogle Scholar
  53. UMS (Umwelt Monitoring Systeme) GmbH (2008) Empfehlungen zur Bodenwasserprobennahme, Version 11/2008. UMS, MünchenGoogle Scholar
  54. WMO (2006) The state of greenhouse gases in the atmosphere using global observations up to December 2004. WMO Greenhouse Bulletin 1. World Meteorological Organization, GenevaGoogle Scholar
  55. Wrage N, Velthof GL, van Beusichem ML, Oenema O (2001) Role of nitrifier denitrification in the production of nitrous oxide. Soil Biol Biochem 33:1723–1732CrossRefGoogle Scholar
  56. Wu X (1999) Popularization of water saving irrigation technique to farmers. In: Xu Z (ed) Proceedings of the international symposium on water-saving irrigation for paddy rice, Guilin, China, pp 41–46Google Scholar
  57. Yamulki S, Jarvis SC (1999) Automated chamber technique for gaseous flux measurements: evaluation of a photoacoustic infrared spectrometer-trace gas analyzer. J Geophys Res 104:5463–5469CrossRefGoogle Scholar
  58. Yan X, Akiyama H, Yagi K (2009) Global estimations of the inventory and mitigation potential of methane emissions from rice cultivation conducted using the 2006. Intergovernmental Panel on Climate Change Guidelines. Global Biogeochem Cycles 23:GB2002CrossRefGoogle Scholar
  59. Yao Z, Zheng X, Dong H, Wang R, Mei B, Zhu J (2012) A 3-year record of N2O and CH4 emissions from a sandy loam paddy during rice seasons as affected by different nitrogen application rates. Agric Ecosyst Environ 152:1–9CrossRefGoogle Scholar
  60. Zou JW, Huang Y, Jiang JY, Zheng XH, Sass RL (2005a) A 3-year field measurement of methane and nitrous oxide emissions from rice paddies in China: effects of water regime, crop residue, and fertilizer application. Global Biogeochem Cycles 19:1–9CrossRefGoogle Scholar
  61. Zou JW, Huang Y, Lu YY, Zheng XH, Wang YS (2005b) Direct emission factor for N2O from rice-winter wheat rotation systems in southeast China. Atmos Environ 39:4755–4765CrossRefGoogle Scholar
  62. Zou JW, Huang Y, Zheng XH, Wang YS (2007) Quantifying direct N2O emissions in paddy fields during rice growing season in mainland China: dependence on water regime. Atmos Environ 41:8030–8042CrossRefGoogle Scholar

Copyright information

© Springer Science+Business Media Dordrecht 2013

Authors and Affiliations

  • Sina Berger
    • 1
  • Inyoung Jang
    • 2
  • Juyoung Seo
    • 2
  • Hojeong Kang
    • 2
  • Gerhard Gebauer
    • 1
  1. 1.Laboratory of Isotope BiogeochemistryBayCEER, University of BayreuthBayreuthGermany
  2. 2.School of Civil and Environmental EngineeringYonsei UniversitySeoulRepublic of Korea

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