Estimates of synthetic fertilizer N-induced direct nitrous oxide emission from Chinese croplands during 1980-2000

被引:62
作者
Zou, Jianwen [1 ]
Lu, Yanyu [1 ,3 ]
Huang, Yao [1 ,2 ]
机构
[1] Nanjing Agr Univ, Coll Resources & Environm Sci, Nanjing 210095, Peoples R China
[2] Chinese Acad Sci, Inst Atmospher Phys, LAPC, Beijing 100029, Peoples R China
[3] Anhui Meteorl Bur, Anhui Climate Ctr, Hefei 230031, Peoples R China
基金
中国国家自然科学基金;
关键词
Chinese cropland; Emission factor; N2O; Synthetic fertilizer; Uncertainty; DIRECT N2O EMISSIONS; RICE-GROWING-SEASON; PADDY FIELDS; INVENTORY;
D O I
10.1016/j.envpol.2009.08.026
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
There is increasing concern that agricultural intensification in China has greatly increased N2O emissions due to rapidly increased fertilizer use. By linking a spatial database of precipitation, synthetic fertilizer N input, cropping rotation and area via GIS, a precipitation-recti fled emission factor of N2O for upland croplands and water regime-specific emission factors for irrigated rice paddies were adopted to estimate annual synthetic fertilizer N-induced direct N2O emissions (FIE-N2O) from Chinese croplands during 1980-2000. Annual FIE-N2O was estimated to be 115.7 Gg N2O-N year(-1) in the 1980s and 210.5 Gg N2O-N year(-1) in the 1990s, with an annual increasing rate of 9.14 Gg N2O-N year(-1) over the period 1980-2000. Upland croplands contributed most to the national total of FIE-N2O, accounting for 79% in 1980 and 92% in 2000. Approximately 65% of the FIE-N2O emitted in eastern and southern central China. (C) 2009 Elsevier Ltd. All rights reserved.
引用
收藏
页码:631 / 635
页数:5
相关论文
共 17 条
[1]   Direct N2O emissions from rice paddy fields:: Summary of available data -: art. no. GB1005 [J].
Akiyama, H ;
Yagi, K ;
Yan, XY .
GLOBAL BIOGEOCHEMICAL CYCLES, 2005, 19 (01) :1-10
[2]  
Bruinsma J., 2017, World Agriculture: Towards 2015-2030, DOI DOI 10.1016/S0264-8377(03)00047-4
[3]   Nitrous oxide emission factors for agricultural soils in Great Britain: the impact of soil water-filled pore space and other controlling variables [J].
Dobbie, KE ;
Smith, KA .
GLOBAL CHANGE BIOLOGY, 2003, 9 (02) :204-218
[4]  
Eggleston S., 2006, IPCC Guidelines for National Greenhouse Gas Inventories, P1
[5]   Modeling methane emission from rice paddies with various agricultural practices [J].
Huang, Y ;
Zhang, W ;
Zheng, XH ;
Li, J ;
Yu, YQ .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2004, 109 (D8) :D081131-12
[6]   Comparing a process-based agro-ecosystem model to the IPCC methodology for developing a national inventory of N2O emissions from arable lands in China [J].
Li, CS ;
Zhuang, YH ;
Cao, MQ ;
Crill, P ;
Dai, ZH ;
Frolking, S ;
Moore B, III ;
Salas, W ;
Song, WZ ;
Wang, XK .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 2001, 60 (1-3) :159-175
[7]   An inventory of N2O emissions from agriculture in China using precipitation-rectified emission factor and background emission [J].
Lu, Yanyu ;
Huang, Yao ;
Zou, Jianwen ;
Zheng, Xunhua .
CHEMOSPHERE, 2006, 65 (11) :1915-1924
[8]  
[Metz B. IPCC IPCC], 2007, CLIMATE CHANGE 2007
[9]  
Solomon S, 2007, AR4 CLIMATE CHANGE 2007: THE PHYSICAL SCIENCE BASIS, P1
[10]   Generating surfaces of daily meteorological variables over large regions of complex terrain [J].
Thornton, PE ;
Running, SW ;
White, MA .
JOURNAL OF HYDROLOGY, 1997, 190 (3-4) :214-251