期刊文献+

改善农学管理措施减少太湖稻麦轮作NH_3和NO排放 被引量:6

Improving Agronomic Practices to Reduce Ammonia and Nitric Oxide Emissions from Rice-wheat Rotation Field in Tai Lake Region,China
下载PDF
导出
摘要 在太湖稻麦轮作体系下,采用密闭室-间歇通气法和静态箱-化学发光法对空白(不施氮肥)、当地常规(农民习惯管理方式)和保产增效(与当地常规相比,改善作物种植、水分和养分管理方式)3个田间小区下的氨(NH_3)挥发和一氧化氮(NO)排放通量进行原位观测,并对作物产量和氮利用率进行评价。结果表明:与当地常规处理相比,保产增效处理在施氮量减少25%的情况下,总作物产量没有降低,且农学利用率提高了39%;NH_3挥发量在稻季和麦季分别减少了26%和44%;NO排放量在稻季较低(N,(0.75±0.03)kg/hm^2),与空白和当地常规处理均没有显著差异(P<0.05),但在麦季则显著降低了49%。因此,保产增效措施不仅能保障高产和提高氮利用率,还能减少NH_3和NO排放,值得在太湖地区推广。 Winter wheat-summer rice rotation is one of the general cropping systems in the Tai Lake Region, China, but which is favor ammonia (NH3) and nitric oxide (NO) emission to atmosphere due to high N input with low N use efficiency (NUE), thus it is necessary to improve the agronomic management practices to alleviate the detrimental impacts of these gaseous compound emissions. This study is to illustrate the effectiveness of an improved integrated crop cultivation, water and nutrient practice for mitigating NH3 and NO emissions. Dynamic and static chambers were employed to simultaneously estimate NH3 and NO emissions from a rice-wheat rotation field with three different treatments of 1) CK (control, without N input), 2) FP (the famer's practice); and 3) IP (the improved crop cultivation, water and nutrient management practice with nitrogen dose reduced by 25% compared to FP in the Tai Lake Region. Crop yield and agronomic N use efficiency (ANUE) were appraised. In the rice-wheat rotation, the total crop yield from IP treatment was consistent with FP, and ANUE increased by 39% (P〈0.05). Compared to FP, IP in the rice and wheat seasons mitigated seasonal NH3 emissions by 26% and 44%, respectively. In meanwhile, IP emitted marginal NO (N 0.75±0.03 kg/hm^2) into the atmosphere in rice growing season, which was in consistent with CK and FP. Besides, IP decreased NO emission by 49% in wheat growing season. Thus, IP practice should be advocated in this region for it sustaining crop yield and decreasing the environmental risk by mitigating significantly NH3 and NO emissions at the same time.
出处 《土壤》 CAS CSCD 北大核心 2015年第5期836-841,共6页 Soils
基金 国家重点基础研究发展计划("973"计划)项目(2013CB127401) 公益性行业(环保)科研专项(201309035) 公益性行业(农业)科研专项(201003014)资助
关键词 氨挥发 一氧化氮排放 稻麦轮作 农学管理 Ammonia volatilization Nitric oxide emission Rice-wheat rotation Agronomic practice
  • 相关文献

参考文献24

  • 1Ju XT, Xing GX, Chen XP, Zhang SL, Zhang L J, Liu X J, Cui ZL, Yin B, Christie P, Zhu ZL, Zhang FS. Reducing environmental risk by improving N management in intensive Chinese agricultural systems[J]. Proceedings of the National Academy of Sciences of the United States of America, 2009, 106(9): 3 041-3 046.
  • 2Zhao X, Xie YX, Xiong ZQ, Yan XY, Xing GX, Zhu ZL. Nitrogen fate and environmental eonsequenee in paddy soil under rice-wheat rotation in the Taihu lake region, China[J]. Plant and Soil, 2009, 319(1/2): 225-234.
  • 3Aneja VP, Roelle PA, Murray GC, Southerland J, Erisman JW, Fowler D, Asman WAH, Patni N. Atmospheric nitrogen compounds II: emissions, transport, transfor- mation, deposition and assessment[J]. Atmospheric Environment, 2001, 35(11): 1 903-1 911.
  • 4Asman WAH, Sutton MA, SchjOrring JK. Ammonia: emission, atmospheric transport and deposition[J]. New Phytologist, 1998, 139(1): 27-48.
  • 5Zheng XH, Huang Y, Wang YS, Wang MX. Seasonal characteristics of nitric oxide emission from a typical Chinese rice-wheat rotation during the non-waterlogged period[J]. Global Change Biology, 2003, 9(2): 219-227.
  • 6Fang SX, Mu YJ. NOx fluxes from three kinds of agricul- tural lands in the Yangtze Delta, China[J]. Atmospheric Environment, 2007, 41(22): 4 766-4 772.
  • 7Mei B, Zheng X, Xie B, Dong H, Zhou Z, Wang R, Deng J, Cui F, Tong H, Zhu J. Nitric oxide emissions from conventional vegetable fields in southeastern China[J]. Atmospheric Environment, 2009, 43(17): 2 762-2 769.
  • 8Stohl A, Williams E, Wotawa G, Kromp-Kolb H. A European inventory of soil nitric oxide emissions and the effect of these emissions on the photochemical formation of ozone[J]. Atmospheric Environment, 1996, 30(22): 3 741- 3 755.
  • 9Fowler D, Pilegaard K, Sutton MA, Ambus P, Raivonen M, Duyzer J, Simpson D, Fagerli H, Fuzzi S, Schjoerring JK, Granier C, Neftel A, Isaksen ISA, Laj P, Maione M, Monks PS, Burkhardt J, Daemmgen U, Neirynck J, Personne E, Wichink-Kruit R, Butterbach-Bahl K, Flechard C, Tuovinen JP, Coyle M, Gerosa G, Loubet B, Altimir N, Gruenhage L, Ammann C, Cieslik S, Paoletti E, Mikkelsen TN, Ro-Poulsen H, Cellier P, Cape JN, Horwith L, Loreto F, Niinemets , Palmer PI, Rinne J, Misztal P, Nemitz E, Nilsson D, Pryor S, Gallagher MW, Vesala T, Skiba U, Briiggemann N, Zechmeister-Boltenstern S, Williams J, O'dowd C, Facchini MC, De LeeuwG, Flossman A, Chaumerliac N, Erisman JW. Atmospheric composition change: Ecosystems-Atmosphere interactions[J]. Atmospheric Environment, 2009, 43(33): 5 193-5 267.
  • 10曾勇军,石庆华,潘晓华,韩涛.施氮量对高产早稻氮素利用特征及产量形成的影响[J].作物学报,2008,34(8):1409-1416. 被引量:77

二级参考文献125

共引文献504

同被引文献154

引证文献6

二级引证文献45

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部