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不同灌溉方式旱田土壤N2O排放和氮素淋溶特征
引用本文:于亚泽,焦燕,杨文柱,宋春妮,于俊霞,刘立家,张婧,刘宇斌.不同灌溉方式旱田土壤N2O排放和氮素淋溶特征[J].中国环境科学,2021,41(2):813-825.
作者姓名:于亚泽  焦燕  杨文柱  宋春妮  于俊霞  刘立家  张婧  刘宇斌
作者单位:1. 内蒙古自治区环境化学重点实验室, 内蒙古 呼和浩特 010022;2. 内蒙古师范大学化学与环境科学学院, 内蒙古 呼和浩特 010022
基金项目:国家自然科学基金资助项目(41765010,41865010,41675140);2019年内蒙古自治区高等学校青年科技英才领军人才(NJYT-20-A04);第十批内蒙古自治区草原英才(2020);2016内蒙古自治区青年创新人才计划项目(2017ZRYB007);内蒙古师范大学研究生科研创新基金资助项目(CXJJS19123)
摘    要:通过野外原位监测试验,利用静态箱-气相色谱法、土壤溶液提取器分别对旱田土壤N2O排放及氮素淋溶进行2018和2019年连续两年观测.试验设计为DCK (滴灌无肥)、DD (滴灌+N 500kg/hm2)、DG (滴灌+N 1000kg/hm2)、FCK (沟灌无肥)、FD (沟灌+N 500kg/hm2)、FG (沟灌+N 1000kg/hm2).结果表明,不同施氮量、不同灌溉方式对N2O排放和氮素淋溶量影响具有极显著差异(P<0.01).N2O排放量随施氮量的增加而增加,滴灌与沟灌相比可有效降低N2O排放,2018和2019年FCK、FD、FG的N2O累积排放量分别为2,23.79,45.73kg/hm2和2.08,6.23,13.93kg/hm2,而DCK、DD、DG分别降低了35%、80.9%、75.6%和26.7%、66.4%、21.5%.2018和2019年旱田土壤氮素淋溶量均表现为:滴灌<沟灌,80cm深度土壤溶液氮素淋溶量<40cm.2018和2019年相同施氮量下滴灌与沟灌相比,在40cm和80cm分别能减少氮素淋溶量36.95%~63.10%和54.93%~87.92%.主成分分析结果表明,影响N2O排放的主要环境因子为土壤NO3--N含量和降水频率,相关系数分别为0.689、0.596;影响氮素淋溶量的主要环境因子为降水频率和灌水频率,相关系数分别为0.697和-0.729.滴灌可有效减少N2O排放和氮素淋溶量,在提高肥料利用率的同时可减轻环境污染.

关 键 词:滴灌  沟灌  氮素淋溶  N2O  NO3--N  NH4+-N  
收稿时间:2020-06-28

Characteristics of N2O emissions and nitrogen leaching from upland soils under drip or furrow irrigation
YU Ya-ze,JIAO Yan,YANG Wen-zhu,SONG Chun-ni,YU Jun-xia,LIU Li-jia,ZHANG Jing,LIU Yu-bin.Characteristics of N2O emissions and nitrogen leaching from upland soils under drip or furrow irrigation[J].China Environmental Science,2021,41(2):813-825.
Authors:YU Ya-ze  JIAO Yan  YANG Wen-zhu  SONG Chun-ni  YU Jun-xia  LIU Li-jia  ZHANG Jing  LIU Yu-bin
Institution:1. Key Laboratory of Environmental Chemistry of Inner Mongolia Autonomous Region, Hohhot 010022, China;2. Chemistry and Environmental Science College, Inner Mongolia Normal University, Hohhot 010022, China
Abstract:In present study, a two-year experiment in the field was performed, and the static chamber and soil solution extractor were used to quantify N2O emissions and nitrogen leaching from upland soils. The treatments include DCK(drip irrigation without fertilizer)、DD(drip irrigation +N 500kg/hm2)、DG(drip irrigation +N 1000kg/hm2)、FCK(furrow irrigation without fertilizer)、FD(furrow irrigation +N 500kg/hm2)、FG(furrow irrigation +N 1000kg/hm2).The results showed that there were significant differences in N2O emissions and nitrogen leaching under different nitrogen fertilizer application and irrigation methods(P<0.01). N2O emissions increased with the increase of nitrogen applications. Compared with furrow irrigation, drip irrigation effectively reduced N2O emissions, the cumulative N2O emissions of FCK、FD、FG were 2, 23.79, 45.73kg/hm2 and 2.08, 6.23, 13.93kg/hm2 in 2018 and 2019, respectively; DCK、DD、DG reduced cumulative N2O emissions by 35%、80.9%、75.6% and 26.7%、66.4%、21.5%, respectively. Cumulative N leaching from upland soils showed that drip irrigation produced less nitrogen leaching than furrow irrigation, nitrogen leached less at the depth of 80cm that at 40cm. Compare with to furrow irrigation, drip irrigation at the depth 40cm、80cm reduced cumulative N leaching amounts (on equivalent N application amounts) by 36.95%~63.10 and 54.93%~87.92% in two years. The results of principal component analysis showed that N2O emissions were mainly determined by soil nitrate nitrogen content and the frequency of precipitation, the correlation coefficients were 0.689 and 0.596, respectively; nitrogen leaching amounts were mainly determined by the frequency of precipitation and irrigation, the correlation coefficients were 0.697 and -0.729, respectively. Drip irrigation effectively reduced the amounts of N2O emissions and nitrogen leaching amounts, at the same time, it could increase nitrogen utilization efficiency and decrease nitrate pollution on the environment.
Keywords:drip irrigation  furrow irrigation  nitrogen leaching  N2O  NO3--N  NH4+-N  
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