Abstract

Abstract. Long-term field observations showed that N2O fluxes observed shortly after N application were not significantly affected by elevated CO2 in the Giessen Free Air Carbon dioxide Enrichment (FACE) study. To further investigate this unexpected result a 15N tracer study was carried out under controlled conditions where in parallel treatments either the NH4+ pool (15NH4NO3) or the NO3− pool (NH415NO3) was enriched with 15N. Fluxes of CO2, CH4, and N2O as well as the 15N enrichment of the N2O were measured. Denitrifying Enzyme Activity (DEA), total denitrification (N2 + N2O) and N2-to-N2O ratios were quantified in separate experiments. Over the 57 day incubation, N2O fluxes averaged 0.090 ng N2O-N g−1 h−1 under ambient and 0.083 ng N2O-N g−1 h−1 under elevated CO2 (not significantly different). The N2O production processes were identified by a two-source model. Results showed that N2O must have also been produced by a third source – possibly related to organic N transformation – which was stimulated by elevated CO2. Soil CO2 fluxes were approximately 20 % higher under elevated CO2 than soil from ambient but the differences were not significant. CH4 oxidation rates were on average −1.75 ng CH4-C g−1 h−1 in the elevated and −1.17 ng CH4-C g−1 h−1 in the ambient indicating that elevated CO2 increased the CH4 oxidation by 49 % compared to ambient CO2 under controlled conditions. N fertilization increased CH4 oxidation by 3-fold in both CO2 treatments. CO2 did not have any significant effect on DEA while total denitrification and N2-to-N2O ratios increased by 36 and 33 %, respectively. The results indicate that shortly after N application elevated CO2 must have stimulated both the N2O production and reduction to N2 to explain the increased N2-to-N2O ratio and at the same time explain the non-responsiveness of the N2O emissions. Thus, the observed variation of the CO2 effect on N2O emissions throughout the year is possibly governed by the dynamics of the N2O reductase activity.

Highlights

  • The level of earth’s atmospheric carbon dioxide (CO2) concentration has risen from ∼280 μl l−1 at the start of the industrial revolution to greater than 385 μl l−1 today, and is expected to exceed 700 μl l−1 by the end of this century (IPCC, 2007)

  • The CH4 oxidation rates before N application were −0.29 to −0.34 ng CH4-C g−1 h−1 in ambient and −0.46 to −0.76 ng CH4-C g−1 h−1 in elevated CO2 soil indicating about a 22 % higher oxidation rate in soil that had been under elevated CO2

  • After N application, the rate of CH4 oxidation increased from −0.21 to −3.1 ng CH4C g−1 h−1 in ambient and −0.45 to −4.26 ng CH4-C g−1 h−1 in elevated CO2

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Summary

Introduction

The level of earth’s atmospheric carbon dioxide (CO2) concentration has risen from ∼280 μl l−1 at the start of the industrial revolution to greater than 385 μl l−1 today, and is expected to exceed 700 μl l−1 by the end of this century (IPCC, 2007). Elevated atmospheric CO2 increases the plant productivity and aboveground biomass resulting in a substantial allocation of carbon (C) to belowground that may lead to a general increase in C inputs in soil. This additional C is likely to fuel belowground microbial processes and may alter both C and N cycling in soil. N2O and CH4 participate in other atmospheric reactions (e.g. stratospheric ozone depletion) of global environmental significance.

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