Ammonia Volatilization and Deriitrification Losses from an Irrigated Maize-Wheat Rotation Field in the North China Plain
Ammonia Volatilization and Denitrilfication Losses from an Irrigated Maize-Wheat Rotation Field in the North China Plain作者机构:InstituteofGeneticsandDevelopmentalBiologyChineseAcademyofSciencesShijiazhuang050021(China) DepartmentofResourceManagementandHorticultureInstituteofLandandFoodResourcetheUniversityofMel-bourneParkville3052Victoria(Australia) InstituteofSoilScienceChineseAcademyofSciencesNanjing210008(China)
出 版 物:《Pedosphere》 (土壤圈(英文版))
年 卷 期:2004年第14卷第4期
页 面:533-540页
核心收录:
学科分类:090101[农学-作物栽培学与耕作学] 09[农学] 0901[农学-作物学]
基 金:Project supported by the Knowledge Innovation Program of the Chinese Academy of Sciences (No. KZCX2-413-3) the National Key Basic Research Support Foundation (NKBRSF) of China (No. G1999011803) the Australian Centre for
主 题:ammonia volatilization denitrification gaseous N loss N_2O emission
摘 要:Ammonia (NH3) volatilization, denitrification loss, and nitrous oxide (N2O) emission were investigated from an irrigated wheat-maize rotation field on the North China Plain, and the magnitude of gaseous N loss from denitrification and NH3 volatilization was assessed. The micrometeorological gradient diffusion method in conjunction with a Bowen Ratio system was utilized to measure actual NH3 fluxes over a large area, while the acetylene inhibition technique (intact soil cores) was employed for measurement of denitrification losses and N2O emissions. Ammonia volatilization loss was 26.62% of the applied fertilizer nitrogen (N) under maize, while 0.90% and 15.55% were lost from the wheat field at sowing and topdressing, respectively. The differences in NH3 volatilization between different measurement events may be due to differences between the fertilization methods, and to differences in climatic conditions such as soil *** losses in the fertilized plots were 0.67%-2.87% and 0.31%-0.49% of the applied fertilizer N under maize and wheat after subtracting those of the controls, respectively. Nitrous oxide emissions in the fertilized plots were approximately 0.08%-0.41% and 0.26%-0.34% of the applied fertilizer N over the maize and wheat seasons after subtracting those of the controls, correspondingly. The fertilizer N losses due to NH3 volatilization were markedly higher than those through denitrification and nitrous oxide emissions. These results indicated that NH3 volatilization was an important N transformation in the crop-soil system and was likely to be the major cause of low efficiencies with N fertilizer in the study area. Denitrification was not a very important pathway of N fertilizer loss, but did result in important evolution of the greenhouse gas N2O and the effect of N2O emitted from agricultural fields on environment should not be overlooked.