Soil N and C trace gas fluxes and microbial soil N turnover in a sessile oak (Quercus petraea (Matt.) Liebl.) forest in Hungary

During two intensive field campaigns in summer and autumn 2004 nitrogen (N₂O, NO/NO₂) and carbon (CO₂, CH₄) trace gas exchange between soil and the atmosphere was measured in a sessile oak (Quercus petraea (Matt.) Liebl.) forest in Hungary. The climate can be described as continental temperate. Fluxes were measured with a fully automatic measuring system allowing for high temporal resolution. Mean N₂O emission rates were 1.5 µg N m^?2 h^?1 in summer and 3.4 µg N m^?2 h^?1 in autumn, respectively. Also mean NO emission rates were higher in autumn (8.4 µg N m^?2 h^?1) as compared to summer (6.0 µg N m^?2 h^?1). However, as NO₂ deposition rates continuously exceeded NO emission rates (?9.7 µg N m^?2 h^?1 in summer and ?18.3 µg N m^?2 h^?1 in autumn), the forest soil always acted as a net NO _x sink. The mean value of CO₂ fluxes showed only little seasonal differences between summer (81.1 mg C m^?2 h^?1) and autumn (74.2 mg C m^?2 h^?1) measurements, likewise CH₄uptake (summer: ?52.6 µg C m^?2 h^?1; autumn: ?56.5 µg C m^?2 h^?1). In addition, the microbial soil processes net/gross N mineralization, net/gross nitrification and heterotrophic soil respiration as well as inorganic soil nitrogen concentrations and N₂O/CH₄ soil air concentrations in different soil depths were determined. The respiratory quotient (ΔCO_2 resp ΔO _{2 resp} ^?1 ) for the uppermost mineral soil, which is needed for the calculation of gross nitrification via the Barometric Process Separation (BaPS) technique, was 0.8978 ± 0.008. The mean value of gross nitrification rates showed only little seasonal differences between summer (0.99 µg N kg^?1 SDW  d^?1) and autumn measurements (0.89 µg N kg^?1 SDW  d^?1). Gross rates of N mineralization were highest in the organic layer (20.1–137.9 µg N kg^?1 SDW  d^?1) and significantly lower in the uppermost mineral layer (1.3–2.9 µg N kg^?1 SDW  d^?1). Only for the organic layer seasonality in gross N mineralization rates could be demonstrated, with highest mean values in autumn, most likely caused by fresh litter decomposition. Gross mineralization rates of the organic layer were positively correlated with N₂O emissions and negatively correlated with CH₄ uptake, whereas soil CO₂ emissions were positively correlated with heterotrophic respiration in the uppermost mineral soil layer. The most important abiotic factor influencing C and N trace gas fluxes was soil moisture, while the influence of soil temperature on trace gas exchange rates was high only in autumn.