Use of 15N natural abundance in nitrogen cycling of terrestrial ecosystems

2013 ◽  
Vol 36 (4) ◽  
pp. 346-352
Author(s):  
Fan-Yun YAO ◽  
Biao ZHU ◽  
En-Zai DU
2006 ◽  
Vol 57 (4) ◽  
pp. 468-475 ◽  
Author(s):  
P. Dijkstra ◽  
O. V. Menyailo ◽  
R. R. Doucett ◽  
S. C. Hart ◽  
E. Schwartz ◽  
...  

1998 ◽  
Vol 4 (7) ◽  
pp. 729-743 ◽  
Author(s):  
M. J. SWIFT ◽  
O. ANDRÉN ◽  
L. BRUSSAARD ◽  
M. BRIONES ◽  
M. -M. COUTEAUX ◽  
...  

2016 ◽  
Vol 113 (42) ◽  
pp. E6391-E6400 ◽  
Author(s):  
Julie Granger ◽  
Scott D. Wankel

Natural abundance nitrogen and oxygen isotopes of nitrate (δ15NNO3and δ18ONO3) provide an important tool for evaluating sources and transformations of natural and contaminant nitrate (NO3−) in the environment. Nevertheless, conventional interpretations of NO3−isotope distributions appear at odds with patterns emerging from studies of nitrifying and denitrifying bacterial cultures. To resolve this conundrum, we present results from a numerical model of NO3−isotope dynamics, demonstrating that deviations in δ18ONO3vs. δ15NNO3from a trajectory of 1 expected for denitrification are explained by isotopic over-printing from coincident NO3−production by nitrification and/or anammox. The analysis highlights two driving parameters: (i) the δ18O of ambient water and (ii) the relative flux of NO3−production under net denitrifying conditions, whether catalyzed aerobically or anaerobically. In agreement with existing analyses, dual isotopic trajectories >1, characteristic of marine denitrifying systems, arise predominantly under elevated rates of NO2−reoxidation relative to NO3−reduction (>50%) and in association with the elevated δ18O of seawater. This result specifically implicates aerobic nitrification as the dominant NO3−producing term in marine denitrifying systems, as stoichiometric constraints indicate anammox-based NO3−production cannot account for trajectories >1. In contrast, trajectories <1 comprise the majority of model solutions, with those representative of aquifer conditions requiring lower NO2−reoxidation fluxes (<15%) and the influence of the lower δ18O of freshwater. Accordingly, we suggest that widely observed δ18ONO3vs. δ15NNO3trends in freshwater systems (<1) must result from concurrent NO3−production by anammox in anoxic aquifers, a process that has been largely overlooked.


2005 ◽  
Vol 75 (2) ◽  
pp. 139-157 ◽  
Author(s):  
Mary S. Booth ◽  
John M. Stark ◽  
Edward Rastetter

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