• ISSN 1008-505X
  • CN 11-3996/S
房福力, 李玉中. 基于同位素特征的华北平原菜地N2O排放监测中取样时间的探讨[J]. 植物营养与肥料学报, 2016, 22(4): 978-987. DOI: 10.11674/zwyf.15146
引用本文: 房福力, 李玉中. 基于同位素特征的华北平原菜地N2O排放监测中取样时间的探讨[J]. 植物营养与肥料学报, 2016, 22(4): 978-987. DOI: 10.11674/zwyf.15146
FANG Fu-li, LI Yu-zhong. Preliminary research on N2O sampling time based on isotopomer signature measurement of vegetable fields in the North China Plain[J]. Journal of Plant Nutrition and Fertilizers, 2016, 22(4): 978-987. DOI: 10.11674/zwyf.15146
Citation: FANG Fu-li, LI Yu-zhong. Preliminary research on N2O sampling time based on isotopomer signature measurement of vegetable fields in the North China Plain[J]. Journal of Plant Nutrition and Fertilizers, 2016, 22(4): 978-987. DOI: 10.11674/zwyf.15146

基于同位素特征的华北平原菜地N2O排放监测中取样时间的探讨

Preliminary research on N2O sampling time based on isotopomer signature measurement of vegetable fields in the North China Plain

  • 摘要: 【目的】为了长期监测土壤释放N2O的通量和同位素变化规律,了解产生N2O的微生物过程,提高对N2O排放量和排放系数估计的准确性,需要对N2O的日变化规律做深入研究,以便获得具有代表性的取样时间点及密闭时间。【方法】采用田间原位试验对华北平原的莴苣菜地进行了N2O排放监测,选取N2O排放高峰期即施肥灌溉后5~6 d为监测时间段,采用静态气体箱收集土壤释放的N2O气体,结合气相色谱和质谱技术测定N2O的含量及其同位素值(δ15N-N2O,δ18O-N2O和SP)。试验设2种取样间隔,即2 h和10 min,分别对N2O日变化规律和密闭时间进行研究。【结果】 1)在莴苣菜地N2O排放高峰期内,N2O通量日变化范围为34.65~131.45 μg/(m2·h),最大和最小的通量分别发生在13: 00和次日5: 00,9: 00的N2O通量为83.66 μg/(m2·h),与日通量平均值82.81 μg/(m2·h)相接近。N2O通量产生日变化的原因与土壤温度有关,相关分析表明,N2O通量与地下5 cm处土壤温度呈显著正相关(R2=0.82, P<0.01),而与土壤充水孔隙度(WFPS)无显著相关性。2)24 h内,δ15Nbulk-N2O和δ18O-N2O随着时间呈现先降低后增加的变化趋势,变化范围分别为-31.22‰~-11.09‰和-7.45‰~-0.68‰; SP值随时间呈现先增加后降低的变化趋势,变化范围为16.13‰~26.41‰。N2O各个同位素值随时间的变化表明产生N2O的微生物过程随之变化,但SP值在9: 00~17: 00较稳定,变化范围为23.26‰~26.21‰,极显著高于其他时刻(P<0.01),表明硝化作用在这一时间段内对N2O的产生起主导作用。3)扣箱40 min后, N2O含量、 δ15N-N2O和SP值都达到稳定状态,因此选取40 min作为单次观测N2O含量和同位素变化的密闭时间。4)24 h内N2O通量加权SP值为22.54‰。根据前人总结的规律,本研究中N2O主要由细菌硝化作用产生,且估计60.92%的N2O来自于细菌硝化作用, 39.08%的N2O来自于反硝化作用。【结论】华北平原莴苣菜地的N2O通量和同位素值具有较大的日变化,综合N2O通量和同位素值,建议选取9: 00作为观测莴苣菜地N2O排放通量和同位素特征值变化规律的时刻,建议静态气体箱密闭时间为40 min。

     

    Abstract: 【Objectives】 Emissions of N2O from vegetable soils are extremely variable in time and therefore there are considerable uncertainties in calculating emission of N2O flux and emission coefficients. It is thus important to investigate the optional sampling time and characteristic of diurnal pattern for N2O. More insights into N2O diurnal variation would also be helpful for long term monitoring of N2O release and for understanding the associated microbiological mechanisms.【Methods】 Field experiment in situ was conducted to study N2O emission after urine amendment and subsequent irrigation for a lettuce production system in North China Plain in 2012. During periods of high N2O fluxes in 5-6 days, N2O emission was collected manually by a closed static flux chamber at two intervals, two hours for diurnal variation and 10 minutes for appropriate enclosure period. N2O concentrations were measured by a gas chromatograph equipped with an electron capture detector (GC-ECD), and isotopomers such as δ15N-N2O, δ18O-N2O and site preference (SP) (difference between the center and the end N atom of the N2O asymmetric molecule) were analyzed and obtained by an elemental analyzer-isotope ratio mass spectrometer(EA-IRMS) system.【Results】 1) During the period of high N2O emission,there was a strong diurnal variation in N2O fluxes ranging from 20.41 to 130.45 μg/(m2·h), with the maximum and minimum values being observed at 1 pm in Apr. 27th and 5 am in Apr. 28th, respectively. Flux measured at 9 am could be used to represent the daily average of the whole day. The fluxes of N2O emitted from the soil were correlated significantly(R2=0.82, P<0.01) with the soil temperature at 5 cm, varied markedly across time, but insignificantly with water filled-pore space (WFPS). 2) Diurnally, the values of δ15Nbulk-N2O and δ18O-N2O decreased first and then increased gradually with time while the values of SP had an opposite trend, suggesting that production processes of N2O were associated with different microbial pathways. Conversely, the stable values of SP of N2O from 9 am through 5 pm indicated that nitrification was the dominant pathway for N2O production. 3) In measuring N2O emission, appropriate enclosure period in the static chamber should be 40 minutes, which was long enough to allow detection of N2O concentration, δ15N-N2O and SP and also short enough to avoid feedback of N2O concentration and microbial pathway change. 4) The calculated emission-weighted site preference was 22.54‰. The N2O emission in this study was dominantly produced from nitrification, contributing 60.9% of the daily totals of N2O emission.【Conclusions】 There were large diurnal variations of N2O concentration and isotopomers from lettuce production system in North China Plain. Considering both values of N2O flux and isotopomers, it was suggested that 9 am was an appropriate time to measure the flux and isotopomer signature of N2O and that enclosure period for one sample event should be 40 minutes.

     

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