Gebauer, G;
Goldberg, S:
N2O sink function in a forest soil as indicated by concentration and stable isotope profiles
Poster, ISOECOL 6, Honolulu, Hawaii: 2008-08-25 - 2008-08-29
Abstract:Nitrous oxide (N
2O) is a potential and long-lasting greenhouse gas of the atmosphere. The atmospheric N
2O concentration currently increases by about 0.3 % per year and reached 319 ppbv in 2005. With a contribution of about 70 % soils act as the main source for atmospheric N
2O. Soil N
2O emissions originate from microbial nitrification and denitrification, with the latter process also potentially being able to consume N
2O. Both processes are mainly driven by soil temperature, soil moisture and substrate availability. Changes in meteorological conditions as predicted for the future are, therefore, expected to affect N
2O emissions from soils.
In this study we investigated effects of experimentally induced drying/rewetting and freeze/thaw events on soil N
2O emissions in a mature Norway spruce forest in the Fichtelgebirge (NE Bavaria, Germany). Drought was induced by roof constructions and freezing by snow removal. The experiments were run in three replicates each. Unmanipulated plots served as controls. In addition to N
2O flux measurements between soil and atmosphere we analysed N
2O concentrations and stable isotope signatures (δ
15N
N2O and δ
18O
N2O) in soil air collected along soil profiles. The latter approach provides information on localisation of N
2O sources and sinks as well as identification of N
2O production and consumption processes.
Drought reduced the N
2O emission from the soil or even turned the forest soil temporarily to an N
2O sink. N
2O emission peaks after rewetting could not compensate for the drought effect. Soil frost caused a burst of N
2O emission.
Soil air N
2O concentration and stable isotope profiles provide a new and hitherto almost unconsidered mechanistic explanation for all of these observations. N
2O concentration in the soil air decreased in most cases exponentially from the subsoil to the soil surface. This observation identifies microbial activity in the subsoil as source for N
2O and diffusion to the soil surface along a concentration gradient. A shift in the N
2O isotope signature along the concentration gradient towards increasingly positive δ values indicates, furthermore, a simultaneous microbial N
2O consumption (reduction to N
2). Drought reduced the source strength of the subsoil for N
2O while simultaneously the sink strength of the topsoil for N
2O remained constant. Both of these factors resulted in the temporary occurrence of below-atmospheric N
2O concentrations in the air of the topsoil and thus a soil sink function for atmospheric N
2O. Frost in the topsoil was the only exception for these trends in N
2O concentration and isotope signature. Under conditions of soil frost the topsoil served no longer as a sink for N
2O, thus leading to the observed burst in N
2O emission.
The until now almost unconsidered sink function of soils for N
2O sheds a new light on the hitherto poorly resolved global N
2O budget. We suggest the consideration of a soil N
2O sink function for future model calculations on global N
2O budgets.