Using field-measured soil N2O fluxes and laboratory scale parameterization of N2O/(N2O+N2) ratios to quantify field-scale soil N2 emissions

被引:31
|
作者
Wang, Rui [1 ]
Pan, Zhanlei [1 ]
Zheng, Xunhua [1 ,2 ]
Ju, Xiaotang [3 ]
Yao, Zhisheng [1 ]
Butterbach-Bahl, Klaus [1 ,4 ]
Zhang, Chong [3 ]
Wei, Huanhuan [3 ]
Huang, Binxiang [3 ]
机构
[1] Chinese Acad Sci, Inst Atmospher Phys, State Key Lab Atmospher Boundary Layer Phys & Atm, Beijing 100029, Peoples R China
[2] Univ Chinese Acad Sci, Coll Earth & Planetary Sci, Beijing 100049, Peoples R China
[3] China Agr Univ, Coll Resources & Environm Sci, Beijing 100193, Peoples R China
[4] Karlsruhe Inst Technol, Inst Meteorol & Climate Res, Atmospher Environm Res, D-82467 Garmisch Partenkirchen, Germany
来源
SOIL BIOLOGY & BIOCHEMISTRY | 2020年 / 148卷 / 148期
基金
中国国家自然科学基金;
关键词
Field N-2 emission; N2O emission; Molar ratio of N2O/(N2O+N-2); Nitrification; Denitrification; Gas-flow-soil-core (GFSC) method; NITROUS-OXIDE; MEASURING DENITRIFICATION; MOLE FRACTION; NITRIC-OXIDE; NITRIFICATION; NITRATE; CO2; NO; REDUCTION; SYSTEMS;
D O I
10.1016/j.soilbio.2020.107904
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Soil dinitrogen (N-2) emissions are a key nitrogen loss pathway of terrestrial ecosystems. However, the quantification of field N-2 emissions from terrestrial ecosystems remains challenging, as sensitive field methods for measuring N-2 fluxes are lacking. Here, we report a new approach to quantify field N-2 emissions by (i) param-eterizing the molar ratio of nitrous oxide (N2O) to N2O plus N-2 emissions (RN2O) in the laboratory and (ii) measuring field N2O emissions and soil factors. Soil samples were taken from a maize field and incubated in the laboratory under simulated field conditions. Soil N-2 and N2O emissions were determined using the gas-flow-soilcore method. The measurements revealed that the RN2O values were significantly higher (0.06-0.67) following urea fertilization and soil rewetting compared to those periods with no fertilization (0.03-0.08) (P < 0.01). A multivariate, nonlinear parameterization of RN z o against four easily measured soil factors (ammonia and nitrate concentrations, temperature, and moisture) (n = 20, r(2) = 0.92, P < 0.001) was developed. The seasonal N-2 emissions at the field scale were calculated by combining the laboratory-measured RN2O with the field-measured N2O emissions and the soil factors. Based on this approach, the cumulative emissions of N-2 and N-2 +N2O for the maize season were 7.2 +/- 2.8 and 9.6 +/- 2.1 (standard error) kg N ha(-1), respectively. Using a fixed RN2O, i.e., disregarding the temporal and spatial variability of RN2O, resulted in approximately 50%-70% lower estimates. Our study shows that a combination of field N2O and soil factors measurements and laboratory parameterization of RN2O allows field N-2 emissions from croplands to be constrained. With additional measurements, including other soil properties, the development of a generalized parameterization of RN2O may become feasible. This approach would allow for a better understanding of gaseous N losses from agricultural ecosystems.
引用
收藏
页数:11
相关论文
共 50 条
  • [21] Field-scale and laboratory study of factors affecting N2O emissions from a rye stubble field on sandy loam soil
    B. J. Jørgensen
    Rasmus N. Jørgensen
    Biology and Fertility of Soils, 1997, 25 : 366 - 371
  • [22] Velocity of N2 upon dissociation of N2O in N2O•(H2O)m
    Gandhi, SR
    JOURNAL OF PHYSICAL CHEMISTRY A, 1999, 103 (50): : 10713 - 10718
  • [23] Temporal in situ dynamics of N2O reductase activity as affected by nitrogen fertilization and implications for the N2O/(N2O + N2) product ratio and N2O mitigation
    Shuping Qin
    Keren Ding
    Tim J. Clough
    Chunsheng Hu
    Jiafa Luo
    Biology and Fertility of Soils, 2017, 53 : 723 - 727
  • [24] Temporal in situ dynamics of N2O reductase activity as affected by nitrogen fertilization and implications for the N2O/(N2O + N2) product ratio and N2O mitigation
    Qin, Shuping
    Ding, Keren
    Clough, Tim J.
    Hu, Chunsheng
    Luo, Jiafa
    BIOLOGY AND FERTILITY OF SOILS, 2017, 53 (07) : 723 - 727
  • [25] DIRECT FIELD MEASUREMENT OF N-2 AND N2O EVOLUTION FROM SOIL
    LIMMER, AW
    STEELE, KW
    WILSON, AT
    JOURNAL OF SOIL SCIENCE, 1982, 33 (03): : 499 - 507
  • [26] NOx AND N2O EMISSIONS FROM SOIL
    Williams, E.
    Hutchinson, G.
    Fehsenfeld, F.
    GLOBAL BIOGEOCHEMICAL CYCLES, 1992, 6 (04) : 351 - 388
  • [27] Transport coefficients and cross sections for electrons in N2O and N2O/N2 mixtures
    Dupljanin, S.
    de Urquijo, J.
    Sasic, O.
    Basurto, E.
    Juarez, A. M.
    Hernandez-Avila, J. L.
    Dujko, S.
    Petrovic, Z. Lj
    PLASMA SOURCES SCIENCE & TECHNOLOGY, 2010, 19 (02):
  • [28] Different pathways of formation of N2O, N2 and NO in black earth soil
    Wolf, I
    Russow, R
    SOIL BIOLOGY & BIOCHEMISTRY, 2000, 32 (02): : 229 - 239
  • [29] N2O emission and the N2O/(N2O + N2) product ratio of denitrification as controlled by available carbon substrates and nitrate concentrations
    Senbayram, M.
    Chen, R.
    Budai, A.
    Bakken, L.
    Dittert, K.
    AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2012, 147 : 4 - 12
  • [30] On the potential of δ18O and δ15N to assess N2O reduction to N2 in soil
    Decock, C.
    Six, J.
    EUROPEAN JOURNAL OF SOIL SCIENCE, 2013, 64 (05) : 610 - 620