[1] Carpenter S R, Caraco N F, Correll D L, et al. Nonpoint pollution of surface waters with phosphorus and nitrogen[J]. Ecol Appl, 1998, 8(3): 559-568.[2] Xu J, Peng S, Yang S, et al. Ammonia volatilization losses from a rice paddy with different irrigation and nitrogen managements[J]. Agr Water Manage, 2012, 104: 184-192.[3] 俞映倞,薛利红,杨林章. 太湖地区稻田不同氮肥管理模式下氨挥发特征研究[J]. 农业环境科学学报,2013,32(8):1 682-1 689.[4] Sun H, Zhang H, Wu J, et al. Laboratory lysimeter analysis of NH3 and N2O emissions and leaching losses of nitrogen in a rice-wheat rotation system irrigated with nitrogen-rich wastewater[J]. Soil Sci, 2013, 178(6): 316-323. [5] 赵冬,颜廷梅,乔俊,等. 稻季田面水不同形态氮素变化及氮肥减量研究[J]. 生态环境学报,2011,20(4):743-749.[6] 张丽娟,马中文,马友华,等. 优化施肥和缓释肥对水稻田面水氮磷动态变化的影响[J]. 水土保持学报,2012,26(1):90-94.[7] 薛利红,俞映倞,杨林章. 太湖流域稻田不同氮肥管理模式下的氮素平衡特征及环境效应评价[J]. 环境科学,2011,32(4): 1 133-1 138.[8] Shang Q, Gao C, Yang X, et al. Ammonia volatilization in Chinese double rice-cropping systems: a 3-year field measurement in long-term fertilizer experiments[J]. Biol Fert Soils, 2014, 50(5): 715-725.[9] Huang P, Zhang J, Zhu A, et al. Coupled water and nitrogen (N) management as a key strategy for the mitigation of gaseous N losses in the Huang-Huai-Hai Plain[J]. Biol Fert Soils, 2014: 1-10.[10] 薛利红,杨林章,施卫明,等. 农村面源污染治理的“4R”理论与工程实践——源头减量技术[J]. 农业环境科学学报,2013,32(5):881-888.[11] 罗利军,梅捍卫,余新桥,等. 节水抗旱稻及其发展策略 [J]. 科学通报,2011,56(11):804-811.[12] Shrestha S, Asch F, Dusserre J, et al. Climate effects on yield components as affected by genotypic responses to variable environmental conditions in upland rice systems at different altitudes[J]. Field Crop Res, 2012, 134: 216-228.[13] 李勇,周毅,尹晓明,等. 不同形态氮素对水稻和旱稻响应水分胁迫的影响[J]. 西北农林科技大学学报:自然科学版,2006,34(5):97-102.[14] Steele K A, Price A H, Witcombe J R, et al. QTLs associated with root traits increase yield in upland rice when transferred through marker-assisted selection[J]. Theor Appl Genet, 2013, 126(1): 101-108.[15] Trijatmiko K R, Prasetiyono J, Thomson M J, et al. Meta-analysis of quantitative trait loci for grain yield and component traits under reproductive-stage drought stress in an upland rice population[J]. Mol Breeding, 2014, 34(2): 283-295.[16] Asai H, Samson B K, Stephan H M, et al. Biochar amendment techniques for upland rice production in Northern Laos: 1. Soil physical properties, leaf SPAD and grain yield [J]. Field Crop Res, 2009, 111(1): 81-84.[17] 邹桂花,梅捍卫,余新桥,等. 不同灌水量对水、旱稻营养生长和光合特性及其产量的影响[J]. 作物学报,2006,32(8):1 179 - 1 183.[18] 侯朋福,李刚华,张国发,等. 养分管理方式对江苏常规粳稻产量和氮素利用率的影响[J]. 土壤,2012,44(2):218-224.[19] 凌启鸿. 水稻精确定量栽培理论与技术[M]. 北京:中国农业出版社,2007.[20] 李刚华,薛利红,尤娟,等. 水稻氮素和叶绿素 SPAD 叶位分布特点及氮素诊断的叶位选择[J]. 中国农业科学,2007,40(6): 1 127-1 134.[21] Sui B, Feng X, Tian G, et al. Optimizing nitrogen supply increases rice yield and nitrogen use efficiency by regulating yield formation factors[J]. Field Crop Res, 2013, 150: 99-107.[22] Mae T. Physiological nitrogen efficiency in rice: nitrogen utilization, photosynthesis, and yield potential[M]//Plant nutrition for sustainable food production and environment. Springer Netherlands, 1997: 51-60.[23] 顾佳,李勇,杨林章,等. 直播水稻田田面水氮素动态变化及径流损失研究[J]. 安徽农业科学,2009,37(8):3 626-3 628.[24] 马立珊,汪祖强,张水铭,等. 苏南太湖水系农业面源污染及其控制对策研究[J]. 环境科学学报,1997,17(1):39-47.[25] 宋勇生,范晓晖,林德喜,等. 太湖地区稻田氨挥发及影响因素的研究[J]. 土壤学报,2004,41(2):265-269. |