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Biology subjects

Ordonez, M. E.

Publications and source records attributed to Ordonez, M. E..

2 recordsLinked to original sources

Burn intensity regulates post-fire effects on soil N2O emissions: A grassland soil pyrocosm study

Post-fire soil emissions of nitric oxide (NO) and nitrous oxide (N2O) are important ecosystem nitrogen (N) loss pathways, but their flux dynamics vary widely across studies, making generalizations challenging. Natural variation in burn intensity--or heat energy released during combustionm--may help resolve this variability by mediating the soil physicochemical and biological drivers of these emissions. Here, we used an experimental "pyrocosm" system to evaluate how varying burn intensity influences post-fire NO and N2O emissions using soil from a Southern California grassland across 18 weeks. Over several months, we measured soil NO and N2O fluxes alongside soil pH, extractable nitrate (NO3-) and ammonium (NH4+), net NH4+ production, net nitrification, soil carbon (C) pools, microbial biomass C, and the potential activities of five extracellular hydrolytic enzymes under Control, Low- (100.1 {+/-} 20.0 oC peak soil temperature at 5 cm depth), and High-intensity (243.8 {+/-} 7.4 oC peak soil temperature at 5 cm depth) burns. Soil NO emissions were not significantly affected by burn intensity. In contrast, N2O emissions tripled under low burn intensity relative to unburned controls, but did not differ from controls at high burn intensity. This stimulation of N2O emission under low burn intensity was driven by increased denitrification, as supported by elevated soil pH and labile C availability, and an 88% reduction in net nitrification that signaled active NO3- consumption. Under high burn intensity, however, severe loss of microbial biomass, soil C, and NO3- constrained denitrification, with rising hydrolytic enzyme activities over time suggesting C limitation. Together, these findings demonstrate that post-fire N2O emissions reflect a fire intensity-dependent balance between microbial mortality and resource limitation, helping to explain divergent N emissions across ecosystems.

ecology↗

Wildfires drive trade-offs in ammonia-oxidizing groups and promote denitrification to increase soil emissions of nitric oxide (NO) and nitrous oxide (N2O) in California chaparral

Wildfires can promote trade-offs in soil nitrifier and denitrifier communities that affect post-fire nitrogen (N) cycling and emissions of nitric oxide (NO), nitrous oxide (N2O), and dinitrogen (N2). For example, by increasing soil pH and ammonium (NH4+), wildfires could increase the abundance of ammonia-oxidizing bacteria (AOB) over archaea (AOA). Because AOB and AOA process N differently, nitrifier trade-offs may affect N emissions and nitrate (NO3-) supply with downstream effects on denitrifier activity, leading us to ask: Do trade-offs between AOA and AOB abundance and shifts in denitrifying processes influence N emissions over time after wildfire? We selectively inhibited AOA and AOB communities from soil collected over four seasonal time points one year before and after a chaparral wildfire and used stable isotopes to parse denitrifier contributions to N2O emissions. Over one year after the wildfire, soil pH increased from 6.1 to 7.0, soil extractable NH4+ increased 30-fold, NO3- increased 5-fold, and NO2- increased 9-fold. AOB amoA gene copy numbers increased 20-fold one year after fire, while AOA abundance remained unchanged. Post-fire soil NO emissions increased 63-fold over one year, with varied contributions from all nitrifier groups. Soil N2O emissions peaked eight months after fire (2271 {+/-} 634 ng N2O-N g-1 soil), with increased contributions from AOA. Wildfire increased {delta}15NSPN2O and {delta}15NbulkN2O values, suggesting increased N2O reduction to N2. Overall, wildfire increased AOB abundance relative to AOA, promoting nitrification activity and providing intermediates to denitrifiers to increase emissions of NO and N2O for up to one year after fire.

ecology↗