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Nitrate transformation and immobilization in particulate organic matter incubations: Influence of redox, iron and (a)biotic conditions

Nitrate can be reduced to other N inorganic species via denitrification and incorporated into organic matter by immobilization; however, the effect of biotic/abiotic and redox condition on immobilization and denitrification processes from a single system are not well documented. We hypothesize nitra...

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Detalles Bibliográficos
Autores principales: Kizewski, Fiona R., Kaye, Jason P., Martínez, Carmen Enid
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Public Library of Science 2019
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6611582/
https://www.ncbi.nlm.nih.gov/pubmed/31276538
http://dx.doi.org/10.1371/journal.pone.0218752
Descripción
Sumario:Nitrate can be reduced to other N inorganic species via denitrification and incorporated into organic matter by immobilization; however, the effect of biotic/abiotic and redox condition on immobilization and denitrification processes from a single system are not well documented. We hypothesize nitrate (NO(3)(-)) transformation pathways leading to the formation of dissolved- and solid-phase organic N are predominantly controlled by abiotic reactions, but the formation of soluble inorganic N species is controlled by redox condition. In this study, organic matter in the form of leaf compost (LC) was spiked with (15)NO(3)(-) and incubated under oxic/anoxic and biotic/abiotic conditions at pH 6.5. We seek to understand how variations in environmental conditions impact NO(3)(-) transformation pathways through laboratory incubations. We find production of NH(4)(+) is predominantly controlled by redox whereas NO(3)(-) conversion to dissolved organic nitrogen (DON) and immobilization in solid-phase N are predominantly controlled by abiotic processes. Twenty % of added (15)N-NO(3)(-) was incorporated into DON under oxic conditions, with abiotic processes accounting for 85% of the overall incorporation. Nitrogen immobilization processes resulted in N concentrations of 4.1–6.6 μg N (g leaf compost)(-1), with abiotic processes accounting for 100% and 66% of the overall (biotic+abiotic) N immobilization under anoxic and oxic conditions, respectively. (15)N-NMR spectroscopy suggests (15)NO(3)(-) was immobilized into amide/aminoquinones and nitro/oxime under anoxic conditions. A fraction of the NH(4)(+) was produced abiotically under anoxic conditions (~10% of the total NH(4)(+) production) although biotic organic N mineralization contributed to most of NH(4)(+) production. Our results also indicate Fe(II) did not act as an electron source in biotic-oxic incubations; however, Fe(II) provided electrons for NO(3)(-) reduction in biotic-anoxic incubations although it was not the sole electron source. It is clear that, under the experimental conditions of this investigation, abiotic and redox processes play important roles in NO(3)(-) transformations. As climatic conditions change (e.g., frequency/intensity of rainfall), abiotic reactions that shift transformation pathways and N species concentrations from those controlled by biota might become more prevalent.