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
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页数:11
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