- Original article
- Open Access
Microbial nitrogen fixation and methane oxidation are strongly enhanced by light in Sphagnum mosses
AMB Express volume 10, Article number: 61 (2020)
Peatlands have acted as C-sinks for millennia, storing large amounts of carbon, of which a significant amount is yearly released as methane (CH4). Sphagnum mosses are a key genus in many peat ecosystems and these mosses live in close association with methane-oxidizing and nitrogen-fixing microorganisms. To disentangle mechanisms which may control Sphagnum-associated methane-oxidation and nitrogen-fixation, we applied four treatments to Sphagnum mosses from a pristine peatland in Finland: nitrogen fertilization, phosphorus fertilization, CH4 addition and light. N and P fertilization resulted in nutrient accumulation in the moss tissue, but did not increase Sphagnum growth. While net CO2 fixation rates remained unaffected in the N and P treatment, net CH4 emissions decreased because of enhanced CH4 oxidation. CH4 addition did not affect Sphagnum performance in the present set-up. Light, however, clearly stimulated the activity of associated nitrogen-fixing and methane-oxidizing microorganisms, increasing N2 fixation rates threefold and CH4 oxidation rates fivefold. This underlines the strong connection between Sphagnum and associated N2 fixation and CH4 oxidation. It furthermore indicates that phototrophy is a strong control of microbial activity, which can be directly or indirectly.
The large amounts of carbon (C) stored in Northern peatlands (representing 250–450 Pg C; Frolking and Roulet 2007) are severely threatened by anthropogenic disturbances of these vulnerable ecosystems due to for example drainage, fires and N-fertilization (Turetsky et al. 2002; Bragazza et al. 2012; Andersen et al. 2013; Abdalla et al. 2016; Leifeld and Menichetti 2018). Over millennia peatlands have acted as net C-sinks, sequestering and storing more C than is emitted to the atmosphere, thereby counteracting global warming (Gorham 1991; Rydin and Jeglum 2006; Frolking and Roulet 2007; Loisel et al. 2014; Leifeld and Menichetti 2018). C is mainly stored as dead organic matter (Loisel et al. 2014) originating moss and plants such as from Sphagnum mosses, Carex species that dominate many of these peatlands.
Most Sphagnum species thrive in nitrogen (N) limited environments (Aerts et al. 1992) and do so by monopolizing the majority of atmospheric N deposited (Fritz et al. 2014). Sphagnum has a high affinity for N (Ks 3.5–6.5 μM) and will rapidly take up ammonium or nitrate when available (Fritz et al. 2014). In addition to the limited pool of environmentally available N, N required for growth is also provided by microbial N2 fixation via Sphagnum-associated microorganisms, which may account for the mismatch between the high N-content of Sphagnum mosses and the low input of N via atmospheric deposition (Vile et al. 2014). In younger peatlands, N2 fixation by methane-oxidizing microorganisms is assumed to be responsible for N accumulation in Sphagnum (Larmola et al. 2014), providing a strong link between the CH4-cycle and N-cycle in Sphagnum-dominated peatlands (Ho and Bodelier 2015).
Worldwide, the N-cycle in peatlands has been disturbed by long-term, anthropogenic N fertilization. This has reduced C-accumulation rates and altered decomposition of stored organic matter (Bragazza et al. 2012) and ultimately leads to changes in the plant-community composition (Tomassen et al. 2004; Fritz et al. 2012). As N-fertilization skews the N:phosphorus (P) ratio in Sphagnum mosses, it was thought that additional P-fertilization might alleviate the effect of N-fertilization. However, this appeared to be only partially true, as mosses remained N-saturated and experienced N-stress despite P-fertilization (Fritz et al. 2012). It is, however, clear that the N-fertilization effect is strongly linked to nutrient stoichiometry, especially in relation to P-availability. Excess N and disturbance of the N:P ratio can greatly affect the delicate balance between C-sink and C-source in peatlands (Turetsky et al. 2002; Frolking et al. 2011; Kivimäki et al. 2013).
The response of the nitrogen-fixing microbial community associated with Sphagnum mosses to N-fertilization remains puzzling. Short-term high N-fertilization has been shown to result in reduced N2 fixation activity in peatland Sphagnum mosses (Kox et al. 2016) as well as in forest mosses (Leppänen et al. 2013). Yet, long-term N-fertilization has been shown to hardly affect N2 fixation in Sphagnum (Kox et al. 2016; van den Elzen et al. 2018). P-fertilization, on the other hand appears to stimulate N2 fixation activity of the associated microorganisms, but not necessarily Sphagnum moss growth (Fritz et al. 2012; van den Elzen et al. 2017; Rousk et al. 2017).
The N-fertilization effect on CH4 oxidation activity depends largely on land use, and the extent and duration of fertilization (Veraart et al. 2015). For bog ecosystems, long term fertilization with N, P and potassium (K) fertilization resulted in increased CH4 emission, mostly via indirect effects such as changes in vegetation structure and peat properties (Juutinen et al. 2018). However, P and K rather than N fertilization seemed to have contributed to this result, since the PK-only treatment of the study stimulated methanogenesis, whereas N fertilization did not affect CH4 production or consumption (Juutinen et al. 2018).
Next to N-fertilization, light intensity and its diurnal rhythm do affect C-sequestration by Sphagnum mosses (Laine et al. 2011; Kangas et al. 2014). Different Sphagnum species are adapted to different light and moisture conditions, which is reflected in their productivity (Kangas et al. 2014; Bengtsson et al. 2016). The diurnal rhythm of Sphagnum mosses influences the conditions in and around the mosses. Although there is little specific literature available on this diurnal effect on the Sphagnum microbiome, it is highly likely that the daily light regime affects the Sphagnum-associated microbiome (Larmola et al. 2014; van den Elzen et al. 2017).
In this study, the primary goal was to investigate the environmental drivers of N2 fixation and CH4 oxidation in pristine Sphagnum mosses. To this end, peat sods were collected from a pristine site in Northern Finland. Fertilization (control, N, P or N + P), CH4, and light treatments were applied in a full factorial set-up to further disentangle the mechanisms controlling Sphagnum-associated CH4 oxidation and N2 fixation. It was expected that N fertilization would result in decreased N2 fixation activity, whereas P fertilization would show increased N2 fixation rates but not necessarily CH4 oxidation rates. Both N2 fixation and CH4 oxidation rates were expected to be higher in light conditions. CH4 addition on the other hand was expected to stimulate methane-oxidizing nitrogen-fixing microorganisms. Moss growth was expected to benefit from any type of fertilization as the mosses were collected from a pristine peat site and thus nutrient limited.
In a climate-controlled room, the peat sods received N, P, both N + P fertilization or no fertilization at all (control) and received additional or no additional CH4. In addition, all measurements were performed in light and dark to test the influence of light. Both in the field and in the lab, we measured net gas fluxes of CO2 and CH4 in dark and light, and determined rates of microbial N2 fixation and CH4 oxidation rates in the dark and light using stable isotopes.
Materials and methods
The sampling site was located in Siikajoki, Finland, a well-studied pristine peatland [N deposition rate locally 0.3 g m−2 year−1; Mustajärvi et al. (2008)] located in the middle of the boreal ecoclimatic zone (64° 45′ N, 24° 42′ E; Tuittila et al. 2013; Larmola et al. 2014). At an oligotrophic fen site SJ4 (Laine et al. 2011) eight peat sods dominated by S. papillosum were collected (50 × 25 × 20 cm; l × w × h) and four 20 L vessels with peat water were collected and transported back to Nijmegen, the Netherlands, within 48 h. Upon arrival in the laboratory, each peat sod was cut into 4 mesocosms which were immediately placed into glass aquaria (25 × 12 × 30 cm; l × w × h), creating 32 mesocosms (25 × 12 × 20 cm; l × w × h). The water level was maintained at 10 cm below the moss surface, which was similar to the natural situation, using the peat water collected locally.
Mesocosms were kept at 15 °C by means of a water bath in a climate chamber (average 24 °C), and exposed to a 16 h light period per day (Philips greenpower LED, Poland) providing approximately 800 µmol PAR m−2 s−1. Mesocosms were acclimatized in the climate chamber for 6 weeks prior to experimental treatment.
Incubations for the determination of N2 fixation and CH4 oxidation rates, both in dark and light conditions, were performed. In the lab, a full factorial set-up was used to study the effect of fertilization, CH4 addition and light as specified in Table 1. Each treatment had 4 replicates, resulting in 32 individual mesocosms; samples originating from one sod did not get the same treatment. The fertilization treatments consisted of artificial rainwater Kox et al. (2016) with additional N fertilization (25 kg N ha−1 year−1 as NH4NO3), P fertilization (10 kg P ha−1 year−1 as KH2PO4), or a combination of both (NP). The non-fertilized controls (C) received limited background levels of N and P (resp. 0.5 kg N ha−1 year−1 as NH4NO3 and 0.2 kg P ha−1 year−1 as KH2PO4). N fertilization was applied by sprinkling the fertilized rainwater on top of the moss layer, whereas P fertilization was supplied via parallel injections (25 times) 1.5 cm below the moss surface mimicking subsurface P fertilization. For the methane treatment, mesocosms received methane (1.3 mmol CH4 L−1) dissolved in artificial rainwater, via the bottom of the mesocosm once a week (1 L). In the control treatment, dissolved Argon was added instead of CH4. The amount of rainwater provided was equalized to the mean annual rainfall in Northern Finland [521 mm year−1; Drebs et al. (2002)]. The experiment lasted for 10 weeks.
Porewater and moss chemistry
Porewater samples were collected via Rhizons (0.2 µm; 5 cm length in the field; Eijkelkamp Agrisearch Equipment, Giesbeek, the Netherlands). Porewater pH, alkalinity, concentrations of PO43−, NO3−, NH4+ and elemental composition were analyzed as described by Van den Elzen et al. (2017). DOC and TN were determined by combustion (Shimadzu, Duisburg, Germany). Upper 3 cm of three Sphagnum specimens were sampled for total N, P and K concentrations in moss tissue, which was analyzed as described by Van den Elzen et al. (2017). All data is presented in Additional file 1: Table S1.
Total gas flux analysis
In the mesocosms, total fluxes of CO2 and CH4 in light and dark were measured using a Picarro G2508 Greenhouse Gas Analyzer with cavity ringdown spectroscopy (Picarro Inc., Santa Clara, CA, USA). When measuring fluxes, mesocosms were closed air-tight using a lid and paste (Terostat IX, Teroson GmbH, Heidelberg, Germany). Temperature and light conditions were logged using a HOBO pendant temperature and light logger (Onset, Bourne, MA, USA). Fluxes are expressed as mg m−2 h−1 for measured rates, but as mg m−2 day−1 for diurnal fluxes, calculated based on 8 h dark and 16 h light regime.
In each mesocosm 2 sticks were placed and marked to determine the height increase of the moss surface. Sphagnum surface height increase relative to each stick was recorded every 2 weeks.
15N2 fixation and 13CH4 oxidation rates
For each activity assay, mosses (top 3 cm length) were carefully collected from each mesocosm. Per incubation three moss parts were put in a 120 ml serum vial, closed with a butyl rubber stopper and crimp capped. To determine nitrogen fixation activity, batch incubations were supplied with 15% labelled 15N–N2. Another set of incubations received 13C-labeled CH4 (5%) which was additionally to the 15% labelled 15N–N2 to determine CH4 oxidation potential. Incubations were kept for 48 h at 24 °C either in the light or in the dark. After incubation, mosses were oven-dried for 48 h at 70 °C and dried material was ground using a mixer mil (MM301, Retsch, Germany) for 2 min at 30 rotations s−1. To determine the fraction of 15N or 13C, plant biomass was taken (resp. 5 and 0.225 mg) in duplicates and analyzed for 15N and 13C content using an elemental (CNS) analyzer coupled to an Isotopic Ratio Mass Spectrometer as described in Kox et al. (2018).
Data was analyzed using R version 3.4.0 (R Development Core Team 2017). Each treatment consisted of 4 replicates (Table 1). Normality of data was tested using Shapiro–Wilk’s test on the residual (stats-package) and homogeneity of variance was tested using Levene’s test (car-package). Data following a normal distribution were analyzed using ANOVA followed by Tukey HSD post hoc test. In case of non-normal or heteroscedastic data, data was transformed prior to analysis. This was the case for N-content (1/n transformation), CO2 flux and CH4 flux in both light and dark conditions (log transformation), 15N–N2 fixation (log transformed), 13C–CH4 oxidation (log-transformed). Data whose distribution remained unaffected upon transformation (C-content, P-content, Porewater) were analyzed using non-parametric tests (Kruskal–Wallis followed by Dunn test).
Here we investigate the environmental drivers of microbial N2 fixation and CH4 oxidation in pristine Sphagnum mosses. Fertilization treatment (Control, N, P, and NP) as well as addition of CH4 and effect of light were applied to further disentangle the mechanisms controlling Sphagnum-associated CH4 oxidation and N2 fixation.
CH4 addition effect
The weekly addition of dissolved CH4 did not significantly change the overall concentration of dissolved CH4 in the mesocosms (CH4 addition 510 ± 42 μmol L−1 (mean ± SEM); no-addition 471 ± 31 μmol L−1; Additional file 1: Figure S1, F1,24 = 0.5, p > 0.05), indicating that sufficient endogenous methane was being produced during the 10 weeks of incubation. Therefore, the results from the CH4 addition and control without methane additions mesocosms were merged in the further analysis, which results in an increase of the number of replicates (resulting in a duplication of samples from 4 to 8, as also indicated in Tables 4, 5 and 6) for each fertilization treatment and light or dark treatment.
NP fertilization effect
The mosses grew on average 0.43 ± 0.02 mm day−1 (equaling 3 cm in 10 weeks; Table 2). Moss growth was not affected by 10 weeks of N, P or N + P fertilization (p > 0.05). C content of the mosses (range 434–444 mg C g−1 dry weight (DW), Table 3) was not affected by the fertilization treatments (χ2(3) = 1.6, p > 0.05), and neither were porewater dissolved organic carbon (DOC, 86–110 ppm) and total N (TN, 1.7–1.9 ppm) (Table 4; DOC F3,28 = 0.82, p > 0.05; TN F3,28 = 0.36, p > 0.05).
The N content of N-fertilized moss (Table 3; N-fertilized 8.1 ± 0.3 mg N g−1; NP fertilized 7.8 ± 0.2 mg N g−1) was about 10% higher (F3,123 = 4.6, p < 0.005) than those of the control and P fertilized plants (control 7.2 ± 0.1 mg N g−1; P fertilized 7.4 ± 0.2 mg N g−1). K-content of the moss biomass showed the opposite pattern, with N fertilized mosses containing 18% less K (F3,123 = 7.87, p < 0.001) compared to non-N-fertilized treatments (Table 3). Analysis of the moss P content revealed that NP fertilized mosses contained 16% more P than all other treatments (Table 3, χ2(3) = 21.7, p < 0.001).
CO2 and CH4 fluxes
CO2 and CH4 fluxes were measured, diurnal fluxes are presented in rates per day and flux rates are presented per hour. The CO2 flux (see Fig. 1a) measured both in dark and light conditions did not differ between treatments (Dark F3,27 = 0.26, p > 0.05; Light F3,28 = 0.33, p > 0.05; Fig. 1a). Overall, diurnal fluxes of all mesocosms showed that these are acting as net CO2 sinks with an average net CO2 intake of 2.5 ± 1.9 mg C m−2 day−1 (Table 5).
The CH4 flux (see Fig. 1b) measured in light conditions was 2.2 times lower in N fertilized (N and N + P) mesocosms (resp. N 3.3 ± 0.8 mg C m−2 h−1 and NP 4.5 ± 1.0 mg C m−2 h−1) compared to non-fertilized mesocosms (control; 9.1 ± 1.7 mg C m−2 h−1; F3,28 = 4.44, p = 0.01). Furthermore, the N fertilized mesocosms showed a higher CH4 flux in the dark (10 ± 3 mg C m−2 h−1), compared to in the light (3.3 ± 0.9 mg C m−2 h−1; F1,48 = 4.25, p < 0.05). The control mesocosms on the other hand showed a lower CH4 flux in the dark (5.1 ± 1.1 mg C m−2 day−1), compared to the light (9.1 ± 1.7 mg C m−2 day−1; see Fig. 1b), which is unlike the fertilized mesocosms. Overall, diurnal CH4 fluxes showed mesocosms were a net source of CH4, with reduced methane emission up to 30% upon N or P fertilization (Table 6).
In the field incubation, N2 fixation rates were 3 times higher in the light than in the dark (resp. 409 ± 112 versus 135 ± 55 nmol N2 g−1 DW day−1; F1,14 = 5.47, p < 0.05; see Fig. 2). This effect was also observed in the mesocosm experiment (15N–N2 F3,58 = 28.23, p < 0.001; 15N–N2 + 13C–CH4 F3.54 = 12.70, p < 0.001; see Fig. 3), where both treatments (N and N + CH4) showed lowest N2 fixation rates in the dark (15N–N2: 21.3 ± 2.1 nmol N2 g−1 DW day−1; 15N–N2 + 13C–CH4: 23.7 ± 2.1 nmol N2 g−1 DW day−1) and highest rates in the light (15N–N2: 89.0 ± 14 nmol N2 g−1 DW day−1; 15N–N2 + 13C–CH4: 54.9 ± 10 nmol N2 g−1 DW day−1). None of the fertilization treatments differed from each other. Yet, it seems that mesocosms which received P and NP fertilization have higher N2 fixation rates on average, even though these are not significantly higher than for the N-fertilization or control.
CH4 oxidation rates as measured by 13C–CH4 incorporation, showed a highly similar pattern to N2 fixation rates. CH4 oxidation was lowest in the dark (81 ± 37 nmol CH4 g−1 DW h−1 Fig. 4) and five times higher in the light (423 ± 64 nmol CH4 g−1 DW h−1; F1,59 = 134.25, p < 0.001). The low CH4 oxidation rate in the dark correlates with high CH4 efflux in the dark. Similar to N2 fixation rates, there was no difference in CH4 oxidation between fertilization treatments.
This study aimed to investigate the effect of various potential environmental drivers on moss growth and associated microbial N2 fixation and CH4 oxidation. Hereto, we fertilized the moss (N, P and N + P) under ambient and increased CH4 concentrations. Additionally, the effect of light was studied. CH4 addition did not increase CH4 concentrations in the mesocosms, indicating that there was always a significant amount of CH4 produced by the methanogenic archaea in the sods. Although fertilization increased nutrient contents in moss tissue, no effect on Sphagnum moss growth was found. In the used set-up, microbial N2 fixation and CH4 oxidation were clearly positively affected by light.
Effects of CH4 on N2 fixation rates
According to our results, it seems that internal CH4 production in the peat sods was already so high that the addition of CH4 became insignificant. Compared to other studies the concentration of CH4 present in the porewater of the mesocosms was already very high (491 ± 26 μmol CH4 L−1), which is similar to the reported maximum values of 407 ± 83 μmol CH4 L−1 (Kip et al. 2012) and more than ten times higher than the 41 μmol CH4 L−1 reported by Putkinen et al. (2014). Similar to CH4 addition in the mesocosms, N2 fixation was also not affected by CH4 addition in the isotope incubations.
Fertilization did not affect CO2 fluxes, but decreased CH4 fluxes in the light, yet measured CH4 oxidation rates were not different between the different fertilization treatments. The moderate effect of N and P fertilization on nutrient content and absence of substantial effects on moss growth might indicate that 10 weeks of fertilization may have been too short to observe an effect. Therefore, a longer period of fertilization or intensified fertilization is advised for future studies and would probably have resulted in notable fertilization effects.
In addition, we supplied P to the mesocosms via injection just below the moss surface (capitula). Although this way of P-fertilization is dissimilar to other studies (Limpens et al. 2004; Fritz et al. 2012; van den Elzen et al. 2017), it resembles the way increased P fluxes enter peat ecosystems in reality. P-fertilization is in most studies sprinkled on top of the mosses or added in the inflowing surface water. These often resulted in a clear P fertilization effect (Fritz et al. 2012; van den Elzen et al. 2017). Most of the surface water entering a peatland, does not reach the capitulum level but only reaches the lower part of the moss. Furthermore, inflow of P into a fen is mostly via surface water. In order to mimick this inflow from P in our mesocosms setup, we decided to inject P instead of sprinkling it on top of the peat sods. The manner of P fertilization does seem to matter for its effect on the plant (Rydin and Clymo 1989). When P fertilization is applied on top of the capitulum more than 90% of the P will remain in the capitulum, whereas fertilization below the capitulum is translocated upwards to the stem and the capitulum and will therefore also become diluted (Rydin and Clymo 1989). If the P fertilization dilutes due to injection below the capitulum, we would have had to fertilize P for a longer period of time to observe any effect. Furthermore, by injecting P-fertilization and sprinkling N-fertilization we separated the two nutrient sources physically from each other. It might be that the physical separation also contributed to the limited fertilization effect. In addition, N and P fertilization should be repeated for a longer period to further test their effects on methane oxidation and nitrogen fixation. In order to compare the results to other studies, these two fertilizers should maybe be added in the same manner.
Light as a key driver of N2 fixation
Three times higher microbial N2 fixation rates and five times higher CH4 oxidation rates in the presence of light indicate that these processes are strongly stimulated by photosynthesis, either directly or indirectly. For leguminous plant species it has recently been reported that the plants modulate their carbon allocation to symbiotic nitrogen-fixing Rhizobia in response to both light an N availability (Friel and Friesen 2019). For N2 fixation associated with Sphagnum, it has been observed before that N2 fixation rates are highest under illuminated conditions (Larmola et al. 2014; van den Elzen et al. 2017). This is true even though N2 fixation is inhibited by presence of O2 (Vitousek et al. 2013). Due to the O2 respiration by the moss in the dark, O2 availability is low in the dark (Kangas et al. 2014), hence dark conditions are in theory more beneficial for N2 fixation. This therefore generates two hypotheses: either N2 fixation activity is mainly performed by phototrophic cyanobacteria, which are most active in light conditions, or the nitrogen-fixing community is (directly or indirectly) dependent on photosynthates produced by the Sphagnum moss in light-conditions. The mechanisms behind this can be disentangled in future research by studying which part of the nitrogen-fixing community is active in the dark versus light by using RNA analysis on the nifH gene.
Light as a key driver of CH4 oxidation
The net CH4 flux is controlled by the CH4 oxidation activity pattern in light and dark. The lower CH4 oxidation activity observed in the dark explains the higher net CH4 flux from the mesocosms in the dark. The light-dependency of moss-associated methanotrophy has been reported before in Sphagnum (Larmola et al. 2014) as well as brown-mosses (Liebner et al. 2011), and it has been reported in a Danish wetland (King 1990), but remains unexplained so-far. Furthermore, N or P fertilization seem to stimulate net CH4 emission in dark but reduces net CH4 emission in light, resulting in a lower CH4 efflux. The extra nutrients in the fertilized mesocosms are causing discrepancy in CH4 oxidation and emission and further underline the intricate role of photosynthesis in the overall CH4 cycle in Sphagnum-dominated peatlands.
We postulate four hypotheses for light-dependent CH4 oxidation observed here. Like N2 fixation, CH4 oxidation is either (1) directly or (2) indirectly dependent on photosynthates produced by moss (and associated photosynthetic microorganisms). In the case of indirect dependency, the photosynthates are affecting another part of the microbial community that the methanotroph subsequently benefits from (Oswald et al. 2015). Regardless of the nature of the dependency, most phototrophs (plants and cyanobacteria) are known to excrete photosynthetic products such as malate, citrate, glycolic acid and methanol (Tolbert and Zill 1956; Nalewajko 1966; Fall and Benson 1996; Meyer et al. 2010; Vorholt 2012). The excretion of carbohydrates is furthermore increased upon photoinhibition to dispose of electrons. Photoinhibition has been shown to occur in Sphagnum and is estimated to result in lowered C accumulation rates (Murray et al. 1993; Mazziotta et al. 2019). Especially in summer, in peatlands in the northern hemisphere photoinhibition might occur, because of the long days and strong light intensity.
The third (3) hypothesis is that CH4 oxidation is directly coupled to microbial photosynthesis (anoxygenic), which has been postulated in the 1960s (Vishniac 1960; Wertlieb and Vishniac 1967) but so far not been experimentally proven yet (Ward et al. 2019). The process has only been reported for Rhodopseudomonas gelatinosa (Wertlieb and Vishniac 1967) but the observed activity was low. A recent study presented metagenomic evidence for the capability of anoxygenic phototrophy by the WPS2 phylum. This phylum, without culture representatives is abundant in the Sphagnum microbiome (Holland-Moritz et al. 2018). Methane would be a suitable and abundant electron donor for anoxygenic phototrophy in peatland ecosystems, much more abundant than the common electron donor in anoxygenic phototrophy, which is sulfide.
The fourth (4) hypothesis is that the methanotrophs might benefit from light-dependent CH4 production, which has been observed in oligotrophic lakes (Grossart et al. 2011) and might as well occur in oligotrophic peatlands. This production of CH4 in daytime in oxygenated lakes has been postulated to be of cyanobacterial origin by cleaving methyl-phosphonates (Tang et al. 2016; Bižić-Ionescu et al. 2020; Günthel et al. 2019). In this way, methanotrophs could thrive when it’s light due to higher concentrations of both CH4 and O2 as a result of oxygenic photosynthesis. In the control treatment of our experiment, CH4 emission rates were indeed almost twice as high in light conditions.
Our study focused on Sphagnum-associated CH4 oxidation and N2 fixation, and the effects of N, P and N + P fertilization, CH4 addition and the additional effect of light. Light was shown to be a strong driver of both N2 fixation and CH4 oxidation, which indicates that both processes benefit directly or indirectly from photosynthesis. Leakage of photosynthates produced by the Sphagnum and associated photosynthetic microbial partners might be a good C-source for the organisms active in CH4 oxidation and N2 fixation. To test the various postulated hypotheses, future research should take a closer look upon the light-dependency of both CH4 oxidation and N2 fixation by measuring changes in activity based upon light on smaller timescales and intervals.
Availability of data and materials
Supplemental data are provided.
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We thank Anna M. Laine for help with arranging the sampling in Finland. Sebastian Krosse and Paul van der Ven from the General Instruments Department Radboud University are thanked for help with elemental analysis of porewater and stable isotope analysis of moss material. David Smit is thanked for help with in the lab with all the treatments in the mesocosm experiment.
MARK was supported by European Research Council Ecomom 339880 to M.S.M.J., who was further supported by the Netherlands Organization for Scientific Research (SIAM Gravitation grant 024 002 002 and Spinoza Award). MAHJvK was supported by a NWO veni grant (016.veni.192.062).
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Kox, M.A.R., van den Elzen, E., Lamers, L.P.M. et al. Microbial nitrogen fixation and methane oxidation are strongly enhanced by light in Sphagnum mosses. AMB Expr 10, 61 (2020). https://doi.org/10.1186/s13568-020-00994-9
- Sphagnum moss