Modeling biomass, nitrogen and water dynamics in rice-wheat rotations

被引:22
作者
Jing, Qi [1 ,2 ,3 ]
van Keulen, Herman [2 ,3 ]
Hengsdijk, Huib [2 ]
机构
[1] Nanjing Agr Univ, Jiangsu Key Lab Informat Agr, Nanjing 210095, Peoples R China
[2] Univ Wageningen & Res Ctr, NL-6700 AP Wageningen, Netherlands
[3] Wageningen Univ, Plant Sci Grp, NL-6700 AK Wageningen, Netherlands
基金
中国国家自然科学基金;
关键词
Soil; Cropping systems; Organic matter; Decomposition; Denitrification; Simulation; SOIL ORGANIC-MATTER; IRRIGATED RICE; EXPLORING OPTIONS; CROPPING SYSTEMS; LOWLAND RICE; CARBON; YIELD; MINERALIZATION; DENITRIFICATION; MANAGEMENT;
D O I
10.1016/j.agsy.2010.04.001
中图分类号
S [农业科学];
学科分类号
09 ;
摘要
Rice-wheat cropping systems occupy between 24 and 26 M ha in Asia. A main feature of RW rotations is the alternation of aerobic and anaerobic soil conditions. This alternation of flooded and non-flooded soil conditions is conducive to N emissions, especially with the current high N rates in RW systems. To design alternative management systems, better understanding of the processes underlying emissions is required. For that purpose, the Rice WhEat Rotation model (RIWER) was developed, on the basis of existing crop, water and soil organic matter models, describing the relevant soil processes under both anaerobic and aerobic conditions. RIWER is evaluated using data from RW experiments in China. Assessment of model performance, on the basis of graphical comparison and goodness-of-fit parameters, showed that RIWER performs well in simulating total aboveground biomass, N uptake of cops and soil inorganic N content. The RIWER modeling framework needs further testing, but offers a promising operational tool to support the design of sustainable RW systems, combining environmentally-friendly production methods and high yields. (C) 2010 Elsevier Ltd. All rights reserved.
引用
收藏
页码:433 / 443
页数:11
相关论文
共 80 条
[1]  
AHMAD MD, 2007, 108 IWMI, P39
[2]  
[Anonymous], 2009, World Population Prospects: The 2008 Revision
[3]  
[Anonymous], 2000, J LAKE SCI, DOI DOI 10.18307/2000.0208
[4]   Non-biomass soil organic N -: the substrate for N mineralization flushes following soil drying-rewetting and for organic N rendered CaCl2-extractable upon soil drying [J].
Appel, T .
SOIL BIOLOGY & BIOCHEMISTRY, 1998, 30 (10-11) :1445-1456
[5]   Denitrification, N2O and CO2 fluxes in rice-wheat cropping system as affected by crop residues, fertilizer N and legume green manure [J].
Aulakh, MS ;
Khera, TS ;
Doran, JW ;
Bronson, KF .
BIOLOGY AND FERTILITY OF SOILS, 2001, 34 (06) :375-389
[6]   Exploring options for water savings in lowland rice using a modelling approach [J].
Belder, P. ;
Bouman, B. A. M. ;
Spiertz, J. H. J. .
AGRICULTURAL SYSTEMS, 2007, 92 (1-3) :91-114
[7]   Stabilization of 13C-carbon and immobilization of 15N-nitrogen from rice straw in humic fractions [J].
Bird, JA ;
van Kessel, C ;
Horwath, WR .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 2003, 67 (03) :806-816
[8]   Modelling the effect of groundwater depth on yield-increasing interventions in rainfed lowland rice in Central Java']Java, Indonesia [J].
Boling, A. A. ;
Bouman, B. A. M. ;
Tuong, T. P. ;
Murty, M. V. R. ;
Jatmiko, S. Y. .
AGRICULTURAL SYSTEMS, 2007, 92 (1-3) :115-139
[9]  
Bouman B.A.M., 2001, ORYZA2000: Modelling Lowland Rice, P235, DOI DOI 10.22004/AG.ECON.281825
[10]   Description and evaluation of the rice growth model ORYZA2000 under nitrogen-limited conditions [J].
Bouman, BAM ;
van Laar, HH .
AGRICULTURAL SYSTEMS, 2006, 87 (03) :249-273