Application of the N2/Ar technique to measuring soil-atmosphere N2 fluxes

被引:15
作者
Yang, Wendy H. [1 ]
Silver, Whendee L. [1 ]
机构
[1] Univ Calif Berkeley, Dept Environm Sci Policy & Management, Ecosyst Sci Div, Berkeley, CA 94720 USA
基金
美国国家科学基金会;
关键词
ANAEROBIC AMMONIUM OXIDATION; ABRUPT CLIMATE-CHANGE; NITROUS-OXIDE; DENITRIFYING BACTERIA; MASS-SPECTROMETER; TRAPPED AIR; FRESH-WATER; ICE CORE; FOREST; DENITRIFICATION;
D O I
10.1002/rcm.6124
中图分类号
Q5 [生物化学];
学科分类号
071010 ; 081704 ;
摘要
RATIONALE: The emission of dinitrogen (N-2) gas from soil is the most poorly constrained flux in terrestrial nitrogen (N) budgets because the high background atmospheric N-2 concentration makes soil N-2 emissions difficult to measure. In this study, we tested the theoretical and analytical feasibility of using the N-2/Ar technique to measure soil-atmosphere N-2 fluxes. METHODS: Dual inlet isotope ratio mass spectrometry was used to measure dAr/N-2 values of gas sampled from surface flux chambers. In laboratory experiments using dry sand in a diffusion box, we induced a known steady-state flux of N-2, and then measured the change in the N-2/Ar ratio of chamber headspace air samples to test our ability to reconstruct this flux. We m\ odeled solubility, thermal, and water vapor flux fractionation effects on the N-2/Ar ratio to constrain physical effects on the measured N-2 flux. RESULTS: In dry sand, an actual N-2 flux of 108 mg N m(-2) day(-1) was measured as 111 +/- 19 mg N m(-2) day(-1) (+/- standard error (SE)). In wet sand, an actual N-2 flux of 160 mg N m(-2) day(-1) was measured as 146 +/- 20 mg N m(-2) day(-1) when solubility and water vapor flux fractionation were taken into account. Corrections for thermal fractionation did not improve estimates of N-2 fluxes. CONCLUSIONS: We conclude that our application of the N-2/Ar technique to soil surface fluxes is valid only above a detection limit of approximately 108 mg N m(-2) day(-1). The N-2/Ar method is currently best used as a validation tool for other methods in ecosystems with high soil N-2 fluxes, but, with future improvements, it holds promise to provide high-resolution measurements in systems with low soil N-2 fluxes. Copyright (C) 2012 John Wiley & Sons, Ltd.
引用
收藏
页码:449 / 459
页数:11
相关论文
共 52 条
[1]  
[Anonymous], 1960, Transport Phenomena
[2]   An improved inlet for precisely measuring the atmospheric Ar/N2 ratio [J].
Blaine, TW ;
Keeling, RF ;
Paplawsky, WJ .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2006, 6 :1181-1184
[3]  
Blake G. R., 1986, Methods of soil analysis. Part 1. Physical and mineralogical methods, P363
[4]  
Boyer EW, 2006, ECOL APPL, V16, P2123, DOI 10.1890/1051-0761(2006)016[2123:MDITAA]2.0.CO
[5]  
2
[6]   Soil core method for direct simultaneous determination of N2 and N2O emissions from forest soils [J].
Butterbach-Bahl, K ;
Willibald, G ;
Papen, H .
PLANT AND SOIL, 2002, 240 (01) :105-116
[7]   Exchange of N-gases at the Hoglwald Forest - A summary [J].
Butterbach-Bahl, K ;
Gasche, R ;
Willibald, G ;
Papen, H .
PLANT AND SOIL, 2002, 240 (01) :117-123
[8]   A note on thermal diffusion. [J].
Chapman, S. ;
Dootson, F. W. .
PHILOSOPHICAL MAGAZINE, 1917, 33 (193-98) :248-253
[9]  
Chapman S., 1970, The mathematical theory of non-uniform gases
[10]   A nitrogen budget for late-successional hillslope tabonuco forest, Puerto Rico [J].
Chestnut, TJ ;
Zarin, DJ ;
McDowell, WH ;
Keller, M .
BIOGEOCHEMISTRY, 1999, 46 (1-3) :85-108