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利用膜进样质谱仪测定水稻土几种厌氧氮转化速率
引用本文:李进芳,柴延超,陈顺涛,单军,颜晓元. 利用膜进样质谱仪测定水稻土几种厌氧氮转化速率[J]. 农业环境科学学报, 2019, 38(7): 1541-1549
作者姓名:李进芳  柴延超  陈顺涛  单军  颜晓元
作者单位:中国科学院南京土壤研究所土壤与农业可持续发展国家重点实验室, 南京 210008;中国科学院大学, 北京 100049,中国科学院南京土壤研究所土壤与农业可持续发展国家重点实验室, 南京 210008,中国科学院南京土壤研究所土壤与农业可持续发展国家重点实验室, 南京 210008;中国药科大学, 南京 210009,中国科学院南京土壤研究所土壤与农业可持续发展国家重点实验室, 南京 210008;中国科学院大学, 北京 100049,中国科学院南京土壤研究所土壤与农业可持续发展国家重点实验室, 南京 210008;中国科学院大学, 北京 100049
基金项目:国家自然科学基金项目(41571289);国家重点研发计划项目(2017YFD0200101);中国科学院战略性先导科技专项(B 类)(XDB15040202);中国科学院南京土壤研究所“一三五”计划领域前沿项目(ISSASIP1653)
摘    要:为了在同一体系下区分和测定水稻土反硝化、厌氧氨氧化(Anammox)和硝酸根异化还原成铵(DNRA)过程发生速率和相互关系,并获取近似原位情况下的净脱氮速率,本研究通过将~(15)NH_4~+化学氧化法测定DNRA速率和添加尿素模拟原位土柱测定净脱氮速率与膜进样质谱法(MIMS)进行联用,完善了一套基于膜进样质谱法(MIMS)的稻田硝态氮转化测定方法体系,利用该方法测定了5种典型的水稻土[辽宁营口(YK)、江苏宜兴(YX)、浙江金华(JH)、广西桂林(GL)和四川广安(GA)]的反硝化、Anammox、DNRA和净脱氮4种氮转化速率。结果显示:基于MIMS的方法体系可实现对水稻土中反硝化、Anammox、DNRA和净脱氮速率的测定,5种水稻土反硝化、Anammox、DNRA和净脱氮速率范围分别为(358.63±25.37)~(479.96±22.12)、(-14.81±0.22)~(5.29±1.22)、(25.76±12.71)~(109.87±3.88)g N·hm~(-2)·h~(-1)和(33.33±11.16)~(72.74±14.18)g N·hm~(-2)·h~(-1),相关结果与其他方法研究结果具有可比性。相关性分析显示:水稻土NO_3~-、可溶性有机碳(DOC)和土壤Fe~(2+)含量是反硝化过程的主要限制因素;NO_3~-是Anammox的关键限制因素;而土壤DOC和Fe~(2+)含量是DNRA过程的主要限制因素。基于MIMS的方法体系可以在短时间内(1周)测定水稻土四种厌氧氮转化速率,且所需样品量低、精确度高,在稻田或湿地土壤厌氧氮转化过程研究中有很好的应用前景。

关 键 词:水稻土  15N示踪  反硝化  厌氧氨氧化  硝酸根异化还原成铵
收稿时间:2018-12-28

Measurement of denitrification, Anammox, DNRA rates, and net N2 flux in paddy soil using a membrane inlet mass spectrometer
LI Jin-fang,CHAI Yan-chao,CHEN Shun-tao,SHAN Jun and YAN Xiao-yuan. Measurement of denitrification, Anammox, DNRA rates, and net N2 flux in paddy soil using a membrane inlet mass spectrometer[J]. Journal of Agro-Environment Science( J. Agro-Environ. Sci.), 2019, 38(7): 1541-1549
Authors:LI Jin-fang  CHAI Yan-chao  CHEN Shun-tao  SHAN Jun  YAN Xiao-yuan
Affiliation:State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China;University of Chinese Academy of Sciences, Beijing 100049, China,State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China,State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China;China Pharmaceutical University, Nanjing 210009, China,State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China;University of Chinese Academy of Sciences, Beijing 100049, China and State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China;University of Chinese Academy of Sciences, Beijing 100049, China
Abstract:Denitrification, anaerobic ammonium oxidation(Anammox), and dissimilatory nitrate reduction to ammonium(DNRA)are the three nitrate reduction processes that largely control the fate of chemical N fertilizers in flooded rice paddies. Previous studies related to the nitrate reduction process mainly focused on one or two independent processes(e.g., denitrification and Anammox), whereas a simultaneous investigation of denitrification, Anammox, and DNRA and their relative contributions to total nitrate removal is lacking. Because of methodological limitations, the near in situ measurement of net N2 flux is also rare. In this study, using membrane inlet mass spectrometry(MIMS) combined with laboratory soil slurry-based 15N tracer and soil core incubation-based N2/Ar techniques, denitrification, Anammox, DNRA,and net N2 flux were investigated in five paddy soils collected from different rice regions of China(Yingkou, YK; Yixing, YX; Jinhua, JH; Guilin, GL; Guangan, GA). The measured rates of denitrification, Anammox, DNRA, and net N2 flux across all paddy soils were(358.63±25.37)~(479.96±22.12),(-14.81±0.22)~(5.29±1.22)(, 25.76±12.71)~(109.87±3.88), and(33.33±11.16)~(72.74±14.18)g N·hm-2·h-1, respectively, which were comparable with previous studies. The soil NO3-, DOC(dissolved organic carbon), and Fe2+ contents were the three dominating factors affecting denitrification. By comparison, the Anammox rates only correlated with the soil NO3- content, whereas the DNRA rates closely related to the soil DOC and Fe2+ content. These results demonstrate that the MIMS combined with laboratory soil slurry-based 15N tracer and soil core incubation-based N2/Ar techniques is a viable, rapid, and precise method for the measurement of denitrification, Anammox, DNRA rates, and net N2 flux in flooded paddy soil, with an obvious advantage that a smaller sample size is required for determination compared to other methods.
Keywords:paddy soil  15N tracer  denitrification  Anammox  DNRA
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