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Full (15)N tracer accounting to revisit major assumptions of (15)N isotope pool dilution approaches for gross nitrogen mineralization

The (15)N isotope pool dilution (IPD) technique is the only available method for measuring gross ammonium (NH(4)(+)) production and consumption rates. Rapid consumption of the added (15)N-NH(4)(+) tracer is commonly observed, but the processes responsible for this consumption are not well understood...

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Detalles Bibliográficos
Autores principales: Braun, Judith, Mooshammer, Maria, Wanek, Wolfgang, Prommer, Judith, Walker, Tom W.N., Rütting, Tobias, Richter, Andreas
Formato: Online Artículo Texto
Lenguaje:English
Publicado: 2017
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6774780/
https://www.ncbi.nlm.nih.gov/pubmed/31579255
http://dx.doi.org/10.1016/j.soilbio.2017.11.005
Descripción
Sumario:The (15)N isotope pool dilution (IPD) technique is the only available method for measuring gross ammonium (NH(4)(+)) production and consumption rates. Rapid consumption of the added (15)N-NH(4)(+) tracer is commonly observed, but the processes responsible for this consumption are not well understood. The primary objectives of this study were to determine the relative roles of biotic and abiotic processes in (15)N-NH(4)(+) sconsumption and to investigate the validity of one of the main assumptions of IPD experiments, i.e., that no reflux of the consumed (15)N tracer occurs during the course of the experiments. We added a (15)N-NH(4)(+) tracer to live and sterile (autoclaved) soil using mineral topsoil from a beech forest and a grassland in Austria that differed in NH(4)(+) concentrations and NH(4)(+) consumption kinetics. We quantified both biotic tracer consumption (i.e. changes in the concentrations and (15)N enrichments of NH(4)(+), dissolved organic N (DON), NO(3)(−) and the microbial N pool) and abiotic tracer consumption (i.e., fixation by clay and/or humic substances). We achieved full recovery of the (15)N tracer in both soils over the course of the 48 h incubation. For the forest soil, we found no rapid consumption of the (15)N tracer, and the majority of tracer (78%) remained unconsumed at the end of the incubation period. In contrast, the grassland soil showed rapid (15)N-NH(4)(+) consumption immediately after tracer addition, which was largely due to both abiotic fixation (24%) and biotic processes, largely uptake by soil microbes (10%) and nitrification (13%). We found no evidence for reflux of (15)N-NH(4)(+) over the 48 h incubation period in either soil. Our study therefore shows that (15)N tracer reflux during IPD experiments is negligible for incubation times of up to 48 h, even when rapid NH(4)(+) consumption occurs. Such experiments are thus robust to the assumption that immobilized labeled N is not re–mobilized during the experimental period and does not impact calculations of gross N mineralization.