[1] Chen X, Cui Z, Fan M, et al. Producing more grain with lower environmental costs. Nature, 2014, 514: 486-489 [2] IPCC. Climate Change 2014, Mitigation of Climate Change, Working Group III Contribution to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge: Cambridge University Press, 2014: 816 [3] Liu Y, Zhou Z, Zhang X, et al. Net global warming potential and greenhouse gas intensity from the double rice system with integrated soil-crop system management: A three-year field study. Atmospheric Environment, 2015, 116: 92-101 [4] Ye L, Qi C, Hong J, et al. Life cycle assessment of polyvinyl chloride production and its recyclability in China. Journal of Cleaner Production, 2017, 142: 2965-2972 [5] Nishimura S, Komada M, Takebe M, et al. Nitrous oxide evolved from soil covered with plastic mulch film in horticultural field. Biology and Fertility of Soils, 2012, 48: 787-795 [6] National Bureau of Statistics of the People’s Republic of China (中华人民共和国国家统计局). China Statistical Yearbook. Beijing: China Statistics Press, 2016 (in Chinese) [7] Wang Y-Q (王艳群), Li Y-C (李迎春), Peng Z-P (彭正萍), et al. Effects of dicyandiamide combined with nitrogen fertilizar on N2O emission and economic benefit in winter wheat and summer maize rotation system. Chinese Journal of Applied Ecology (应用生态学报), 2015, 26(7): 1999-2006 (in Chinese) [8] Ma Y, Kong X, Yang B, et al. Net global warming potential and greenhouse gas intensity of annual rice-wheat rotations with integrated soil-crop system management. Agriculture, Ecosystems & Environment, 2013, 164: 209-219 [9] Liu J, Bu L, Zhu L, et al. Nitrogen fertilization effects on nitrogen balance and use efficiency for film-mulched maize in a semiarid region. Acta Agriculturae Scandinavica, 2013, 63: 612-622 [10] Mosier A, Halvorson A, Reule C, et al. Net global warming potential and greenhouse gas intensity in irrigated cropping systems in Northeastern Colorado. Journal of Environmental Quality, 2006, 35: 1584-1598 [11] IPCC. Climate Change 2013: The Physical Science Basis, Working Group I. Contribution to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge: Cambridge University Press, 2013 [12] Zhang W, Dou Z, He P, et al. New technologies reduce greenhouse gas emissions from nitrogenous fertilizer in China. Proceedings of the National Academy of Sciences of the United States of America, 2013, 110: 8375-8380 [13] Brentrup F, Pallière C. Greenhouse gas emission and energy efficiency in European nitrogen fertilizer production and use. Cambridge, United Kingdom: International Fertiliser Society Conference, 2008 [14] National Bureau of Statistics of the People’s Republic of China (中华人民共和国国家统计局). China Statistical Yearbook. Beijing: China Statistics Press, 2011 (in Chinese) [15] Yue S-C (岳善超). Optimum Nitrogen Management for High-yielding Wheat and Maize Cropping System. PhD Thesis. Beijing: China Agricultural University, 2013 (in Chinese) [16] Williams J, Crozier C, White J, et al. Comparison of soil nitrogen tests for corn fertilizer recommendations in the humid Southeastern USA. Soil Science Society of America Journal, 2007, 71: 171-180 [17] Zheng H, Huang H, Yao L, et al. Impacts of rice varieties and management on yield-scaled greenhouse gas emissions from rice fields in China: A meta-analysis. Biogeosciences, 2014, 10: 19045-19069 [18] Jennifer P, Hwang H, Jessie G, et al. Impact of plastic film mulching on increasing greenhouse gas emissions in temperate upland soil during maize cultivation. Applied Soil Ecology, 2015, 91: 48-57 [19] Okuda H, Noda K, Sawamoto T, et al. Emission of N2O and CO2 and uptake of CH4 in soil from a Satsuma mandarin orchard under mulching cultivation in central Japan. Engei Gakkai Zasshi, 2007, 76: 279-287 [20] Liu J, Zhu L, Luo S, et al. Response of nitrous oxide emission to soil mulching and nitrogen fertilization in semi-arid farmland. Agriculture, Ecosystems and Environment, 2014, 188: 20-28 [21] Yi Q (易 琼), Huang X (黄 旭), Zhang M (张 木), et al. Effects of nitrogen application rate and sources on yield of lettuce and nitrous oxide emission in vegetable soil. Journal of Agro-Environment Science (农业环境科学学报), 2016, 35(10): 2019-2025 (in Chinese) [22] Liu Y, Li Y, Wan Y, et al. Nitrous oxide emissions from irrigated and fertilized spring maize in semi-arid northern China. Agriculture, Ecosystems & Environment, 2011, 141: 287-295 [23] Zhong D, Chen F, Zhang H, et al. Effects of nitrogen application rates on net annual global warming potential and greenhouse gas intensity in double-rice cropping systems of the Southern China. Environmental Science and Pollution Research, 2016, 23: 24781-24795 [24] Berger S, Kim Y, Kettering J, et al. Plastic mulching in agriculture: Friend or foe of N2O emissions. Agriculture, Ecosystems and Environment, 2013, 167: 43-51 [25] Schimel J. Global change: Rice, microbes and methane. Nature, 2000, 403: 375-377 [26] Zhang Z, Chen J, Liu T, et al. Effects of nitrogen fertili-zer sources and tillage practices on greenhouse gas emissions in paddy fields of central China. Atmospheric Environment, 2016, 144: 274-281 [27] Linquist B, Adviento-Borbe M, Pittelkow C, et al. Fertilizer management practices and greenhouse gas emissions from rice systems: A quantitative review and analysis. Field Crops Research, 2012, 135: 10-21 [28] Mer J, Roger P. Production, oxidation, emission and consumption of methane by soils: A review. European Journal of Soil Biology, 2001, 37: 25-50 [29] Mosier A, Halvorson A, Reule C, et al. Net global warming potential and greenhouse gas intensity in irrigated cropping systems in northeastern Colorado. Journal of Environmental Quality, 2006, 35: 1584 [30] Liu Y, Zhou Z, Zhang X, et al. Net global warming potential and greenhouse gas intensity from the double rice system with integrated soil-crop system management: A three-year field study. Atmospheric Environment, 2015, 116: 92-101 [31] Dai Y, Di H, Cameron K, et al. Effects of nitrogen application rate and a nitrification inhibitor dicyandiamide on methanotroph abundance and methane uptake in a grazed pasture soil. Environmental Science & Pollution Research, 2013, 20: 8680-8690 [32] Liu J, Chen X, Zhan A, et al. Methane uptake in semiarid farmland subjected to different mulching and nitrogen fertilization regimes. Biology & Fertility of Soils, 2016, 52: 1-10 [33] Gan Y, Liang C, Wang X, et al. Lowering carbon footprint of durum wheat by diversifying cropping systems. Field Crops Research, 2011, 122: 199-206 [34] Huang Y, Tang Y. An estimate of greenhouse gas (N2O and CO2) mitigation potential under various scenarios of nitrogen use efficiency in Chinese croplands. Global Change Biology, 2010, 16: 2958-2970 [35] Haque M, Kim G, Kim P, et al. Comparison of net global warming potential between continuous flooding and midseason drainage in monsoon region paddy during rice cropping. Field Crops Research, 2016, 193: 133-142 [36] Chen H, Liu J, Zhang A, et al. Effects of straw and plastic film mulching on greenhouse gas emissions in Loess Plateau, China: A field study of 2 consecutive wheat-maize rotation cycles. Science of the Total Environment, 2017, 579: 814-824 [37] Liu J, Bu L, Lin Z, et al. Optimizing plant density and plastic film mulch to increase maize productivity and water-use efficiency in semiarid areas. Journal of Agronomy, 2014, 106: 1138-1146 [38] Rossner H, Ritz C, Astover A. Optimisation of fertiliser rates in crop production against energy use indicators. European Journal of Agronomy, 2014, 55: 72-76 [39] Bu L, Liu J, Zhu L, et al. Attainable yield achieved for plastic film-mulched maize in response to nitrogen deficit. European Journal of Agronomy, 2014, 55: 53-62 [40] Burney J, Davis S, Lobell D. From the Cover: Greenhouse gas mitigation by agricultural intensification. Proceedings of the National Academy of Sciences of the United States of America, 2010, 107: 12052-12057 |