Response of C and N cycles to N fertilization in Sphagnum and Molinia-dominated peat mesocosms
Graphical abstract
Introduction
Peatlands currently act as a major long-term carbon (C) sink ecosystem. Although these wetlands cover only 3% of the land area, they have stored a third of the global soil C since the early Holocene (Turunen et al., 2002). Most Sphagnum peatlands (up to 80%) are located at high latitudes of the northern hemisphere in the cool temperate zone in association with waterlogged, nutrient poor conditions and the presence of Sphagnum mosses (e.g. Gorham, 1991). To cope with low nutrient concentrations, Sphagnum mosses have developed mechanisms to efficiently use nutrients thanks to their high cation exchange capacity, nutrient translocation and atmospheric interception, reducing the nutrient availability to vascular plants (e.g. Turetsky et al., 2012). However, northern temperate ecosystems receive four times more airborne nitrogen (N) today than 150 years ago (Holland et al., 1999, Lamarque et al., 2005). Increased N deposition leads to a progressive N saturation of Sphagnum mosses, thus favoring the invasion of vascular plants and reducing Sphagnum moss growth (Limpens et al., 2011). Such changes seem to reduce the C sequestration rates in peatlands (Bragazza et al., 2006, Gunnarsson et al., 2008), even if they increase the vascular plants' productivity (Wu et al., 2015). However, the effect of the increase in N loads on stocks and exchanges of N and C are still understudied in peatlands, although they are known to generally increase N2O emissions to the atmosphere (e.g. Nykänen et al., 2002, Francez et al., 2011). Peatland C-storage capacity is often considered alone to assess the effects of climate change on peatlands without considering the N stored in the ecosystems that could account for a significant N2O source and therefore act as a positive feedback to climate change (Repo et al., 2009).
The increase in vascular plant cover due to human activities such as nutrient supply, e.g., atmospheric N deposition, or drainage, increases organic matter decomposition (Gogo et al., 2016) and modulates CO2 and CH4 emissions in peatlands (Ward et al., 2013, Leroy et al., 2017). The combined effects of vascular plant invasion with N deposition on both C and N cycles and stocks still remain to be elucidated. N fertilization generally stimulates the vascular plant biomass, thereby contributing to higher primary production. However, it also leads to a higher decomposition rate due to a reduction in the C/N ratio and more root exudates that generate additional respiration (Wu et al., 2015). Our aim was therefore to assess the effect of N supply on both C and N dynamics in peat mesocosms collected in a Sphagnum-dominated peatland invaded by a vascular plant, Molinia caerulea. All the peat mesocosms contained Sphagnum rubellum, and half of them also contained M. caerulea. Half of each plant community mesocosm was subjected to an increase in N deposition by a weekly amendment to reach an addition of 3.2 g N/(m2·year). Thus, the hypotheses investigated are that N deposition will lead to the following processes under the two plant communities:
- (i)
Processes involving the C cycle: (a) an increase in C fluxes by promoting ecosystem respiration (ER) due to a faster decomposition of plant tissues containing more N (Bragazza et al., 2006); (b) stimulation of the gross primary production (GPP) by an enhancement of both Sphagnum mosses and graminoid biomass (e.g. Tomassen et al., 2003, Granath et al., 2009); (c) a rise in CH4 emissions through a higher OM decomposition and increase in root exudates.
- (ii)
Processes involving the N cycle: (a) higher concentrations of the dissolved NH4+ and NO3− and of the N stored by Sphagnum mosses; (b) an increase in N2O emissions under both plant communities (Roobroeck et al., 2010).
- (iii)
Processes involving M. caerulea occurrence: an increase in the C fluxes in peatlands (CO2, CH4) and DOC content and a decrease in the ecosystem C sink function compared to Sphagnum-dominated peatland due to the promotion of peat decomposition (Leroy et al., 2017).
Section snippets
Experimental design
Twelve peat mesocosms (depth and diameter: 30 cm) were collected in March 2015 at La Guette peatland, an acidic fen invaded by M. caerulea (pH about 4, 47°19′44″N, 2°17′04″E, France). The mean annual precipitation and temperature of La Guette peatland are 883 mm and 11 °C, respectively (Gogo et al., 2011). The mesocosms were buried outdoors (N 47°50′01″, E 1°56′34″, ISTO, Orléans) and surrounded with a tarpaulin containing water from the peatland. Air and soil temperature at 5 and 20 cm depth
C and N fluxes
No significant differences in ER, GPP, CH4 emissions or [DOC] were observed between the Control and Fertilized mesocosms for the two plant communities (Table 1). Hypothesis (i), which assumed a promotion of ER, GPP and CH4 emissions, must therefore be rejected. Differences were driven only by the plant communities: the presence of M. caerulea increased the gaseous C fluxes (ER, GPP, CH4 emissions) compared to Sphagnum mesocosms (Table 1). Furthermore, the number and height of M. caerulea leaves
N retention by Sphagnum
The number and height of M. caerulea leaves were similar between the Control and the Fertilized mesocosms and no stimulation of Molinia growth was observed. This is in agreement with the results of Tomassen et al. (2003) who found an effect of N addition on M. caerulea biomass only after 3 years of N input. In addition, the different forms of N dissolved in peat water were not affected by the N addition treatment (Table 1). However, N addition induced an increase in the concentration and stock
Conclusions
Increasing N deposition did not impact the C fluxes (CO2, CH4), [DOC], stocks or above-ground biomass of M. caerulea in this short-term experiment. This was due to the high capacity of Sphagnum mosses to intercept atmospheric N, limiting the N input effect. Despite the low N availability, NH4NO3 addition promoted N2O emissions, which were also influenced by the vegetation composition with the lowest emissions with M. caerulea occurrence. This modification in N2O emissions probably results from
Acknowledgments
This paper is a contribution to the research conducted in the Labex VOLTAIRE (ANR-10-LABX-100-01). The authors gratefully acknowledge the financial support provided to the PIVOTS project by the Région Centre – Val de Loire: ARD 2020 program, CPER 2015 -2020 and the European Union who invests in Centre-Val de Loire with the European Regional Development Fund. This work is also supported by the AMIS (FAte and IMpact of AtmospherIc PollutantS) project funded by the European Union, under the Marie
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