Effects of nitrogen fertiliser and wheat straw application on CH4 and N2O emissions from a paddy rice field
J. Ma A C , X. L. Li A C , H. Xu A , Y. Han A , Z. C. Cai A and K. Yagi BA State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
B National Institute of Agro-Environmental Sciences, 3-1-1, Kannondai, Tsukuba 305, Japan.
C Graduate University of Chinese Academy of Sciences, Beijing 100049, China.
D Corresponding author. Email: hxu@issas.ac.cn
Australian Journal of Soil Research 45(5) 359-367 https://doi.org/10.1071/SR07039
Submitted: 21 March 2007 Accepted: 12 July 2007 Published: 16 August 2007
Abstract
A 3-year field experiment was conducted to study the effects of nitrogen fertiliser and straw application on CH4 and N2O emissions from a paddy rice field in China from 2003 to 2005. Three rates of nitrogen fertiliser (0, 200, and 270 kg N/ha) and 2 levels of wheat straw (0 and 3.75 × 103 kg/ha) were adopted in this experiment. The effect of nitrogen fertiliser application on CH4 emission seemed to be affected by application rate. Nitrogen fertiliser decreased CH4 emission relative to the control when applied at a rate of 200 kg N/ha, but the effect lessened if the application rate was further increased to a rate of 270 kg N/ha. The depressive effect of nitrogen fertiliser application on CH4 emissions from rice fields became more pronounced when wheat straw was also incorporated with fertiliser, compared with nitrogen fertiliser application alone. Straw incorporation significantly enhanced CH4 emission by 3–11 times (P < 0.05). Nitrogen fertiliser application increased N2O emission by 5–6 times when applied at a rate of 200 kg N/ha and by 10–14 times when applied at a rate of 270 kg N/ha. On average, straw incorporation tended to decrease N2O emission by about 30% significant (P > 0.05). More than 50% of seasonal total amount of N2O was emitted within 11 days after fertiliser application at panicle initiation. The global warming potential caused by both CH4 and N2O emissions was affected by nitrogen fertiliser application rate and significantly stimulated by wheat straw incorporation. The global warming potential was lowest when nitrogen fertiliser was applied at a rate of 200 kg N/ha.
Additional keyword: GWP.
Acknowledgments
This work was funded by the National Natural Science Foundation of China (Grant No. 40621001 and 40671094). The authors express their sincere gratitude to the responsible editors and anonymous reviewers for their corrections and suggestions to the manuscript.
Avalakki UK,
Strong WM, Saffigna PG
(1995) Measurements of gaseous emissions from denitrification of applied nitrogen-15. II. Effects of temperature and added straw. Australian Journal of Soil Research 33, 89–99.
| Crossref | GoogleScholarGoogle Scholar |
Baggs EM,
Rees RM,
Smith KA, Vinten AJA
(2000) Nitrous oxide emission from soils after incorporating crop residues. Soil Use and Management 16, 82–87.
Bender M, Conrad R
(1995) Effect of CH4 concentration and soil conditions on the induction of CH4 oxidation activity. Soil Biology & Biochemistry 27, 1517–1527.
| Crossref | GoogleScholarGoogle Scholar |
Bronson KF,
Neue HU,
Singh U, Abao EB
(1997) Automated chamber measurement of CH4 and N2O flux in a flooded rice soil. I. Effect of organic amendments, nitrogen source, and water management. Soil Science Society of America Journal 61, 981–987.
Cai ZC
(1997) A category for estimate of CH4 emission from rice paddy fields in China. Nutrient Cycling in Agroecosystems 49, 171–179.
| Crossref | GoogleScholarGoogle Scholar |
Cai ZC,
Laughlin RJ, Stevens RJ
(2001) Nitrous oxide and dinitrogen emissions from soil under different water regimes and straw amendment. Chemosphere 42, 113–121.
| Crossref | GoogleScholarGoogle Scholar | PubMed |
Cai ZC,
Shen GY,
Yan XY,
Tsuruta H,
Yagi K, Mimami K
(1998) Effects of soil texture, soil temperature and Eh on methane emissions from rice paddy fields. ACTA Pedologica Sinica 35, 145–154.
Cai ZC,
Tsuruta H, Minami K
(2000) Methane emission from rice fields in China: measurements and influencing factors. Journal of Geophysical Research 105, 17231–17242.
| Crossref | GoogleScholarGoogle Scholar |
Cai ZC,
Xing GX,
Shen GY,
Xu H,
Yan XY,
Tsuruta H,
Yagi K, Minami K
(1999) Measurements of CH4 and N2O emissions from rice paddies in Fengqiu, China. Soil Science and Plant Nutrition 45, 1–13.
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 fertilizers and water management. Plant and Soil 196, 7–14.
| Crossref | GoogleScholarGoogle Scholar |
Cai ZC, Yan XY
(1996) Simulation of methane oxidation by paddy soils in a closed system. Pedosphere 6, 313–320.
Cai ZC, Yan XY
(1999) Kinetic model for methane oxidation by paddy soil as affected by temperature, moisture and N addition. Soil Biology & Biochemistry 31, 715–725.
| Crossref | GoogleScholarGoogle Scholar |
Chen GX,
Huang GH,
Huang B,
Yu KW,
Wu J, Xu H
(1997) Nitrous oxide and methane emissions from soil–plant systems. Nutrient Cycling in Agroecosystems 49, 41–45.
| Crossref | GoogleScholarGoogle Scholar |
Dobbie KE,
McTaggart I, 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, 26891–26900.
| Crossref | GoogleScholarGoogle Scholar |
Huang Y,
Zou JW,
Zheng XH,
Wang Y, Xu XK
(2004) Nitrous oxide emissions as influenced by amendment of plant residues with different C : N ratios. Soil Biology & Biochemistry 36, 973–981.
| Crossref | GoogleScholarGoogle Scholar |
Huang YZ,
Zhang FZ,
Liu SQ, Cao MQ
(1999) Effect of allelochemicals on N2O emission from soil. ACTA Scientiae Ciecumstantiae 19, 478–482 [In Chinese].
Jiang JY,
Huang Y, Zong LG
(2003) Influence of water controlling and straw application on CH4 and N2O emissions from rice field. China Environmental Science 23, 552–556 [In Chinese].
Kightley D,
Nedwell DB, Cooper M
(1995) Capacity for methane oxidation in landfill cover soils measured in laboratory-scale soil microcosms. Applied and Environmental Microbiology 61, 592–601.
| PubMed |
Kludze HK,
Delaune RD, Patrick WH
(1993) Aerenchyma formation and methane and oxygen exchange in rice. Soil Science Society of America Journal 57, 386–391.
Lindau CW,
Bollich PK,
deLaune RD,
Patrick WH, Law VJ
(1991) Effect of urea fertilizer and environmental factors on CH4 emissions from a Louisiana, USA rice field. Plant and Soil 136, 195–203.
| Crossref | GoogleScholarGoogle Scholar |
Mosier A,
Wassmann R,
Verchot L,
King J, Palm C
(2004) Methane and nitrogen oxide fluxes in tropical agricultural soils: sources, sinks and mechanisms. Environment, Development and Sustainability 6, 11–49.
| Crossref | GoogleScholarGoogle Scholar |
Mulvaney RL,
Khan SA, Mulvaney CS
(1997) Nitrogen fertilizers promote denitrification. Biology and Fertility of Soils 24, 211–220.
| Crossref | GoogleScholarGoogle Scholar |
Nishimura S,
Sawamoto T,
Akiyama H,
Sudo S, Yagi K
(2004) Methane and nitrous oxide emissions from a paddy field with Japanese conventional water management and fertilizer application. Global Biogeochemical Cycles 18, GB2017.
| Crossref | GoogleScholarGoogle Scholar |
Sass RL, Fisher FM
(1997) Methane emissions from rice paddies: a process study summary. Nutrient Cycling in Agroecosystems 49, 119–127.
| Crossref | GoogleScholarGoogle Scholar |
Schimel J
(2000) Global change: rice, microbes and methane. Nature 403, 375–377.
| Crossref | GoogleScholarGoogle Scholar | PubMed |
Syamsul Arif MA,
Houwen F, Verstraete W
(1996) Agricultural factors affecting methane oxidation in arable soil. Biology and Fertility of Soils 21, 95–102.
| Crossref | GoogleScholarGoogle Scholar |
Wang ZP,
Delaune RD,
Lindau CW, Patrick WH
(1992) Methane production from anaerobic soil amended with rice straw and nitrogen fertilizers. Fertilizer Research 33, 115–121.
| Crossref | GoogleScholarGoogle Scholar |
Wang ZP,
Delaune RD,
Masschelegn PH, Patrick WH
(1993) Soil redox and pH effects on methane production in flooded rice soils. Soil Science Society of America Journal 57, 382–385.
Xing GX
(1998) N2O emission from cropland in China. Nutrient Cycling in Agroecosystems 52, 249–254.
| Crossref | GoogleScholarGoogle Scholar |
Xiong ZQ,
Xing GX,
Tsuruta H,
Shen GY,
Shi SL, Du LJ
(2002) Field study on nitrous oxide emissions from upland cropping systems in China. Soil Science and Plant Nutrition 48, 539–546.
Xu H,
Xing GX,
Cai ZC, Tsuruta H
(1997) Nitrous oxide emissions from three rice paddy fields in China. Nutrient Cycling in Agroecosystems 49, 267–272.
| Crossref | GoogleScholarGoogle Scholar |
Yagi K, Minami K
(1990) Effect of organic matter application on methane emission from some Japanese paddy fields. Soil Science and Plant Nutrition 36, 599–610.
Yan X,
Du L,
Shi S, Xing G
(2000) Nitrous oxide emission from wetland rice soil as affected by the application of controlled-availability fertilizers and mid-season aeration. Biology and Fertility of Soils 32, 60–66.
| Crossref | GoogleScholarGoogle Scholar |
Yu K,
Chen G, Patrick WH
(2004a) Reduction of GWP contribution from a rice field by irrigation, organic matter, and fertilizer management. Global Biogeochemical Cycles 18, GB3018.
| Crossref | GoogleScholarGoogle Scholar |
Yu K,
Chen G, Patrick WH
(2004b) Redox window with minimum GWP contribution from rice soils. Soil Science Society of America Journal 68, 2086–2091.
Zhong HP,
Yue YZ, Fan JW
(2003) Characteristics of crop straw resources in China and its utilization. Resources Science 25, 62–67 [In Chinese].
Zou GY,
Zhang F,
Chen XP,
Ju XT,
Liu XJ, Pan JR
(2001) Effect of straw addition on denitrification in upland soil. Review of Chinese Agricultural Science and Technology 3, 47–50 [In Chinese].