首页 | 本学科首页   官方微博 | 高级检索  
     检索      

土壤中羟胺和亚硝态氮非生物过程对N_2O排放的贡献
引用本文:马 兰,李晓波,李博伦,颜晓元.土壤中羟胺和亚硝态氮非生物过程对N_2O排放的贡献[J].土壤学报,2016,53(5):1181-1190.
作者姓名:马 兰  李晓波  李博伦  颜晓元
作者单位:1. 土壤与农业可持续发展国家重点实验室 中国科学院南京土壤研究所,南京 210008; 中国科学院大学,北京 100049;2. 土壤与农业可持续发展国家重点实验室 中国科学院南京土壤研究所,南京 210008; 中国科学院华南植物园退化生态系统植被恢复与管理重点实验室,广州 510650;3. 土壤与农业可持续发展国家重点实验室 中国科学院南京土壤研究所,南京,210008
基金项目:国家自然科学基金项目(41425005,41401279)和土壤与农业可持续发展国家重点实验室(中国科学院南京土壤研究所)开放基金(Y412201422)资助
摘    要:羟胺(NH_2OH)和亚硝态氮(NO_2~--N)均可以通过非生物过程产生N_2O,但是同一土壤中其对N_2O排放的相对贡献尚不明确。本文采用高压灭菌和室内培养方法,测定了采自6个不同地点的农业利用土壤在灭菌和非灭菌条件下添加NH_2OH或NO_2~--N后N_2O的排放量,以研究土壤中NH_2OH和NO_2~--N非生物过程对N_2O排放的相对贡献及其关键因子。结果表明,供试土壤中,NH_2OH非生物过程产生的N_2O贡献介于6%~73%,NO_2~--N非生物过程产生N_2O占的比例为3%~236%;在pH7的衢州茶园、鹰潭旱地、常熟菜地和海伦旱地土壤中,添加NO_2~--N后非生物过程产生N_2O比例大于添加NH_2OH的处理,但是在pH7的常熟果园和封丘旱地土壤中则相反;pH是影响NH_2OH和NO_2~--N非生物过程产生N_2O的关键因子,添加NH_2OH处理中非生物过程产生N_2O占N_2O总排放量的比例与土壤pH呈正相关(p0.05),而在添加NO_2~--N处理中呈负相关(p0.01)。上述结果说明,NO_2~--N在偏酸性土壤中可能主要通过非生物过程产生N_2O,而在偏碱性土壤中主要通过生物过程;NH_2OH则与之相反。

关 键 词:氧化亚氮(N2O)  羟胺(NH2OH)  亚硝态氮(NO2--N)  非生物-生物过程
收稿时间:2/2/2016 12:00:00 AM
修稿时间:2016/6/16 0:00:00

Contributions of Abiotic Processes Driven by Hydroxylamine and Nitrite to N2O Emission in Six Different Types of Soils in China
MA Lan,LI Xiaobo,LI Bolun and YAN Xiaoyuan.Contributions of Abiotic Processes Driven by Hydroxylamine and Nitrite to N2O Emission in Six Different Types of Soils in China[J].Acta Pedologica Sinica,2016,53(5):1181-1190.
Authors:MA Lan  LI Xiaobo  LI Bolun and YAN Xiaoyuan
Institution:Institute of Soil Science, Chinese Academy of Sciences,South China Botanical Garden, Chinese Academy of Sciences,Institute of Soil Science, Chinese Academy of Sciences,Institute of Soil Science, Chinese Academy of Sciences
Abstract:Objective]Nitrous oxide(N2O)is an important greenhouse gas contributing to global warming and depleting stratospheric ozone. Agricultural soils are the major sources of anthropogenic N2O emissions. N2O emitted from natural and cultivated soils is mainly generated through nitrification and denitrification,accounting for about 70% of the global total,but contributions of other processes(such as chemodenitrification)are poorly understood. Hydroxylamine(NH2OH)and nitrite(NO2--N)are two main intermediate products of nitrification,and the latter is also an intermediate product of denitrification,both of which can produce N2O through abiotic processes. However,relative contributions of these two products to N2O emission in the same soil remain unclear.Method]To determine contributions of the two products, NH2OH and NO2--N,through abiotic processes in soil to emission of N2O and to identify related affecting factors,an indoor incubation experiment was designed and carried out,using soil samples collected from a tea garden in Quzhou,an upland field in Yingtan,a vegetable garden in Changshu,an upland field in Hailun,an orchard in Changshu and an upland field in Fengqiu,representing four types of land use. The soil samples,sterilized(autoclaved three times at 121℃ for 1 h before nitrogen fertilization)and unsterilized, were spiked with NH2OH or NO2--N,separately,and incubated. Emissions of N2O from the soil samples were monitored after 2 hours of incubation.Result]Addition of NH2OH or NO2--N increased N2O emission from each tested soil,with N2O flux peaking 2 h after the addition of NH2OH during the observed period, and the highest peak was observed from the soil samples collected from the orchard in Changshu Orchard (1 585μg kg-1 h-1). N2O emissions from the soils spiked with NO2--N varied in the range of 6.42~61.28μg kg-1 h-1 in flux. In unsterilized or natural soil samples spiked with NH2OH,N2O emission coefficients varied from 18.63% to 35.95%,which were 10.03 times~76.46 times that in the soil samples spiked with NO2--N. Effect of sterilization on N2O emission differed between the soil samples spiked with NH2OH and their respective ones spiked with NO2--N. Sterilization significantly reduced N2O emission in all the soil samples spiked with NH2OH,especially in the soil samples from the tea garden in Quzhou,with the reduction reaching,up to 94%,while in the soil samples spiked with NO2--N,the effect of sterilization was observed only in those from Changshu and Fengqiu,but reverse effects were found in those from Quzhou,Yingtan, Changshu and Hailun. In all the soil samples,abiotic processes of NH2OH contributed 6%~73% to total of N2O emission,whereas abiotic process of NO2--N did 3%~236%. In the soil samples from Quzhou, Yingtan,Changshu and Hailun,all being higher than 7 in pH,abiotic process of NO2--N contributed more than abiotic process of NH2OH did to N2O emission but in the soil samples from Changshu and Fengqiu, both being higher than 7 in pH too,reverse trends were found,indicating soil pH is a key factor affecting abiotic N2O production from NH2OH or NO2--N. In the soil samples spiked with NH2OH,the contribution of abiotic process,in terms of proportion,to the total N2O emission was significantly and positively related to soil pH(p< 0.05),while in the soil samples spiked with NO2--N,it was negatively related(p< 0.01).Conclusion]All the above-describedfindings suggest that the formation of N2O from NO2--N is probably mainly attributed to abiotic processes in acid soils and to biotic processes in alkaline soils,while the formation of N2O from NH2OH goes just the opposite.
Keywords:Nitrous oxide (N2O)  Hydroxylamine (NH2OH)  Nitrite (NO2--N)  Biotic-abiotic process
本文献已被 CNKI 万方数据 等数据库收录!
点击此处可从《土壤学报》浏览原始摘要信息
点击此处可从《土壤学报》下载免费的PDF全文
设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号