4.7 Article

Application of a triple 15N tracing technique to elucidate N transformations in a UK grassland soil

Journal

GEODERMA
Volume 385, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.geoderma.2020.114844

Keywords

Nitrous oxide; Denitrification; Nitrification; Heterotrophic nitrification

Categories

Funding

  1. Biotechnology and Biological Sciences Research Council (BBSRC)
  2. UK Biotechnology and Biological Sciences Research Council (BBSRC) [BBS/E/C/00010310, BBS/E/C/000I0320, BB -J0042861]
  3. BBSRC [BB/K001051/1]
  4. Stapledon Memorial Trust
  5. Agencia Nacional de Investigacion e Innovacion
  6. INIA-Uruguay
  7. la Caixa Banking Foundation
  8. BBSRC [BB/K001051/1, BBS/E/C/000I0310, BBS/E/C/000I0320] Funding Source: UKRI

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This study quantifies the production and consumption pathways of N2O in soil using labelled substrate-N, showing the impact of different water filled pore space on N-transformation processes and emissions. The research highlights the importance of heterotrophic nitrification and denitrification in the N2O emissions, demonstrating the complex relationship between water filled pore space and nitrogen transformations.
To identify the production and consumption pathways and temporal dynamics of N2O emitted from soil, this study uses N-15-labelled substrate-N to quantify the underlying gross N transformation rates using the Ntrace analysis tool and link them to N-emissions. In three experiments twelve soil cores each were incubated in a lab incubation system to measure gaseous emissions, while parallel incubations under the same conditions were set up for destructive soil sampling at 7 time points. Using the triple labelling technique (applying NH4NO3 with either the NH4+-N or the NO3--N or both being N-15 labelled), this study investigated the effects of 55, 70 and 85% water filled pore space (deemed to promote nitrification, both nitrification and denitrification, and denitrification, respectively) in a clay soil on gaseous N emissions and investigates the source and processes leading to N2O emissions. To assess the utilisation of applied NO3- vs. nitrified NO3- from applied NH4+, the N-15 tracing tool Ntrace was used to quantify the rates of immobilisation of NO3- and NH4+, oxidation of NH4+, mineralisation of organic N and subsequent nitrification by the analysis of the N-15 in the soil. Gross transformation rates were calculated, indicating the relative importance of added NO3- and NO3- derived from nitrified added NH4+. Results show an important contribution of heterotrophic nitrification (organic N oxidation to NO3-) which was highest at the 55% water filled pore space (WFPS), decreasing in its contribution to N-transformation processes with increasing WFPS, while nitrification (NH4+ oxidation to NO3-) was contributing the most at 70% WFPS. The contribution of denitrification increased with increasing WFPS, but only became dominant at 85% WFPS. While denitrification still showed to be most important at high and nitrification at lower WFPS, the actual % WFPS values were not as expected and highlight the fact that WFPS is a contributor, but not the sole/most important parameter determining the type of N-transformation processes taking place.

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