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Isotopic overprinting of nitrification on denitrification as a ubiquitous and unifying feature of environmental nitrogen cycling

239

Citations

68

References

2016

Year

Abstract

Natural abundance nitrogen and oxygen isotopes of nitrate (δ<sup>15</sup>N<sub>NO3</sub> and δ<sup>18</sup>O<sub>NO3</sub>) provide an important tool for evaluating sources and transformations of natural and contaminant nitrate (NO<sub>3</sub><sup>-</sup>) in the environment. Nevertheless, conventional interpretations of NO<sub>3</sub><sup>-</sup> 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 NO<sub>3</sub><sup>-</sup> isotope dynamics, demonstrating that deviations in δ<sup>18</sup>O<sub>NO3</sub> vs. δ<sup>15</sup>N<sub>NO3</sub> from a trajectory of 1 expected for denitrification are explained by isotopic over-printing from coincident NO<sub>3</sub><sup>-</sup> production by nitrification and/or anammox. The analysis highlights two driving parameters: (i) the δ<sup>18</sup>O of ambient water and (ii) the relative flux of NO<sub>3</sub><sup>-</sup> 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 NO<sub>2</sub><sup>-</sup> reoxidation relative to NO<sub>3</sub><sup>-</sup> reduction (>50%) and in association with the elevated δ<sup>18</sup>O of seawater. This result specifically implicates aerobic nitrification as the dominant NO<sub>3</sub><sup>-</sup> producing term in marine denitrifying systems, as stoichiometric constraints indicate anammox-based NO<sub>3</sub><sup>-</sup> production cannot account for trajectories >1. In contrast, trajectories <1 comprise the majority of model solutions, with those representative of aquifer conditions requiring lower NO<sub>2</sub><sup>-</sup> reoxidation fluxes (<15%) and the influence of the lower δ<sup>18</sup>O of freshwater. Accordingly, we suggest that widely observed δ<sup>18</sup>O<sub>NO3</sub> vs. δ<sup>15</sup>N<sub>NO3</sub> trends in freshwater systems (<1) must result from concurrent NO<sub>3</sub><sup>-</sup> production by anammox in anoxic aquifers, a process that has been largely overlooked.

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