Abstract

Abstract. A 5-year greenhouse gas (GHG) exchange study of the three major gas species (CO2, CH4 and N2O) from an intensively managed permanent grassland in Switzerland is presented. Measurements comprise 2 years (2010 and 2011) of manual static chamber measurements of CH4 and N2O, 5 years of continuous eddy covariance (EC) measurements (CO2–H2O – 2010–2014), and 3 years (2012–2014) of EC measurement of CH4 and N2O. Intensive grassland management included both regular and sporadic management activities. Regular management practices encompassed mowing (three to five cuts per year) with subsequent organic fertilizer amendments and occasional grazing, whereas sporadic management activities comprised grazing or similar activities. The primary objective of our measurements was to compare pre-plowing to post-plowing GHG exchange and to identify potential memory effects of such a substantial disturbance on GHG exchange and carbon (C) and nitrogen (N) gains and losses. In order to include measurements carried out with different observation techniques, we tested two different measurement techniques jointly in 2013, namely the manual static chamber approach and the eddy covariance technique for N2O, to quantify the GHG exchange from the observed grassland site. Our results showed that there were no memory effects on N2O and CH4 emissions after plowing, whereas the CO2 uptake of the site considerably increased when compared to pre-restoration years. In detail, we observed large losses of CO2 and N2O during the year of restoration. In contrast, the grassland acted as a carbon sink under usual management, i.e., the time periods 2010–2011 and 2013–2014. Enhanced emissions and emission peaks of N2O (defined as exceeding background emissions 0.21 ± 0.55 nmol m−2 s−1 (SE = 0.02) for at least 2 sequential days and the 7 d moving average exceeding background emissions) were observed for almost 7 continuous months after restoration as well as following organic fertilizer applications during all years. Net ecosystem exchange of CO2 (NEECO2) showed a common pattern of increased uptake of CO2 in spring and reduced uptake in late fall. NEECO2 dropped to zero and became positive after each harvest event. Methane (CH4) exchange fluctuated around zero during all years. Overall, CH4 exchange was of negligible importance for both the GHG budget and the carbon budget of the site. Our results stress the inclusion of grassland restoration events when providing cumulative sums of C sequestration potential and/or global warming potential (GWP). Consequently, this study further highlights the need for continuous long-term GHG exchange observations as well as for the implementation of our findings into biogeochemical process models to track potential GHG mitigation objectives as well as to predict future GHG emission scenarios reliably.

Highlights

  • Grassland ecosystems are commonly known for their provisioning of forage, either directly via grazing of animals on-site or indirectly by regular biomass harvest and preparation of silage or hay

  • Existing studies have compared the two measurement techniques employed in this study in grasslands before and estimated annual emissions based on differing methodologies (Flechard et al, 2007; Jones et al, 2017)

  • This study in combination with an overview of available datasets on grassland restoration and their consequences for greenhouse gas (GHG) budgets highlights the overall need for additional observational data

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Summary

Introduction

Grassland ecosystems are commonly known for their provisioning of forage, either directly via grazing of animals on-site or indirectly by regular biomass harvest and preparation of silage or hay. Datasets containing continuous measurements of all three major GHGs (CO2, CH4 and N2O) in grassland ecosystems remain limited (Hörtnagl et al, 2018), include a single GHG only, or focus on specific management activities (Fuchs et al, 2018; Krol et al, 2016). In contrast to CO2 exchange that showed large net uptake rates in spring, N2O emissions were largest during summer (JJA) and lowest in winter (DJF). Annual sums showed a net uptake of CO2 during the 2 pre-plowing years (−695 g CO2 and −978 g CO2 m−2 yr−1 in 2010 and 2011, respectively). Up to 3 times this net uptake was reached in 2013 and 2014, the 2 post-plowing years (−2046 g CO2 and −2751 g CO2 m−2 yr−1, Table 2). The plowing year 2011 was characterized by a net release of CO2 (1447 g CO2 m−2 yr−1)

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