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Automatic Chamber Measurements of Methane and Carbon Dioxide Fluxes and Isotopologues of CH4 in a sub-Arctic Mire Ryan D. 1* Lawrence , Carmody K. 2 McCalley , Patrick M. 3 Crill , Ruth K. 4 Varner , Scott R. 2 Saleska 1Department of Chemistry, Geology, and Physics, Elizabeth City State University, Elizabeth City, NC 27909, USA. (*[email protected]) 2Department of Ecology and Evolutionary Biology, University of Arizona, Tucson, AZ 85719, USA. 3Department of Geological Sciences, University of Stockholm, Svante Arrhenius Va ̈g 8 C, SE-10691 Stockholm, Sweden. 4 Climate Change Research Center, Institute for the Study of Earth, Oceans and Space, Morse Hall, University of New Hampshire, Durham, NH 03824, USA. INTRODUCTION METHODOLOGY Northern peatlands currently store ~30% of the world’s soil carbon and are the largest single natural source of atmospheric methane (CH4) Since 2000, the Swedish sub-Arctic mean annual temperature has crossed the significant 0 C threshold1 Individual automated chamber measurements were conducted using two 5 minute interval lid closures, under two different light conditions: I. Ambient light [transparent chamber] (Figure 5*) II. Darkened [shrouded chamber] (Figure 6) Methane isotopic composition derived from Keeling regressions of isotope and concentration data from automated chamber flux measurement the atmospheric concentrations of both greenhouse gases2 cryospheric and ecological processes1 Table I. Automated Chamber Ecosystem Chamber # Ecosystem 1, 3, 5 2, 4, 6 palsa Sphagnum 7, 8, 9 Eriophorum Methane has 62 times the global warming potential (GWP) of CO2 at 20 year timescales3 In wetland systems, CH4 emissions are highly variable (both spatially and temporally)4,5 In terrestrial freshwater systems, CH4 is formed by two main pathways: CH3COOH → CH4 + CO2 Fig. 6 Darkened chamber *chamber lid open in photo Equation I: Acetate Fermentation; dominates freshwater systems 6 / Eriophorum sites 7 II. 2CH2O + 2H2O → 2CO2 + 4H2 CO2 + 4H2 → CH4+ 2H2O III. 2CH2O → CH4 + CO2 Fig. 5 Ambient light chamber Time Equation II: Reduction of CO2 with Hydrogen; dominates Sphagnum sites 7 Equation III: Overall reaction encompassing both pathways of CH4 production # of Sampling Days 7 2 4 09:00 – 15:00 12:00 – 18:00 21:00 – 03:00 Table III. Automated Chamber Measurements Measurement Type Table II. Sample Time Period * In addition, entire automated chamber system was calibrated every 90 minutes. * One complete cycle (Chamber 1-9) is three hours. As the landscape transitions from a dry palsa, underlain by permafrost, to a predominately wet site dominated by Eriophorum spp. I. Sequestration of CO2 II. Increasing amount of CH4 to the atmosphere δ13C-CH4 was determined using a Quantum Cascade Laser Spectrometer (QCL) As the climate warms, possible positive feedbacks driven by changes in peatland carbon dioxide (CO2) and CH4 cycling could have major impacts on I. CONCLUSION Light Condition Ambient Dark NEE Respiration ✓ ✓ ✓ CH4 Exchange ✓ ✓ δ13C-CH4 ✓ ✓ The average carbon isotope composition of emitted CH4 was -68 ‰ at the Sphagnum site compared to -62 ‰ at the Eriophorum site I. Depicts relative shift from CO2-reductive towards acetate fermentation 6 Isotopic signature of derive CH4 appears to not be affected by light conditions FUTURE WORK More measurements should be conducted, especially during the 21:00 – 03:00 time period larger data sets will begin to offset the the high variability of CH4 emissions provide more information about potential impact of light on δ13C-CH4 Collect active layer depth8, water table depth4,9, chamber plant species composition by percent cover8,6, and pH8 if suitable for site Aforementioned variables shown to affect CH4 exchange and CO2 dynamics Further analyze data using a statistical package, such as SPSS or SAS Example : paired t-test of average day vs. night δ13C-CH4 to determine if isotopic composition of derived CH4 source is affected by light Examine CH4 exchange Flux measurements Eriophorum palsa -20 NEE -65 Respiration -25.93 -44.83 -110 GPP -78.41 -77.39 -200 -150.77 First and foremost, I would like to thank God for without him truly none of this would have been possible. 6 4 2 1.17 0.02 Figure 7) GPP was calculated using the equation GPP = NEE – respiration. From permafrost to Eriophorum, more plants result in overall uptake of CO2. -62 -64 -70 -68.61 -67.95 -72 -74 -66.98 -67.65 All Measurements Day (0900-1500) Night (2100-0300) Eriophorum Site δ13C-CH4 Dark -56 -57 -58 -59 All Measurments Day (0900-1500) Night (2100-0300) -60 -61 -62 -63 -72.33 -61.49 -60.87 -61.63 -62.26 -62.48 -64 -76 -65 -78 -66 -63.27 Figure 9 & 10) The averages of all δ13C-CH4 within each cover type are similar; however, measurements conducted during the hours of 09:00 – 15:00 vs. 21:00 – 03:00 may potentially be significantly different. Yet, CH4 high variability may heavily influence results of small sample size (n = 24). Fig. 2) Fig. 3) Fig. 4) Thanks to Mr. E. Froburg, NERU collaborators, and NSF for making this research experience possible. To Ms. Kaitlyn Steele, I most graciously appreciate the selflessness actions and contributions to the overall success of the NERU 2012. Figures 1- 4 provided by Maria Paula (MP) Mugnani..Figures 5 & 6 provided by Dr. Ruth K. Varner. This research was supported through the Northern Ecosystems Research for Undergraduates (NERU) program (NSF REU site EAR#1063037). Ambient Light -60 -67.18 0.00 Figure 8) Methane flux measurements were made under ambient light and shrouded conditions. Differences in CH4 emission occur; however, high variability and small sample size may reason that result in observed change. Dark -66 Ambient Flux Dark Flux 0 Sphagnum Site δ13C-CH4 Ambient Light 1.56 -4 -219.38 -290 -68 ACKNOWLEDGEMENT 6.33 -2 -245 Measure δ13C-CH4 of emitted CH4 5.51 33.23 25 -155 Sphagnum Eriophorum 8 69.23 51 70 δ13C-CH4 (‰) Elevated, dry palsa underlain by permafrost) (Figure 2) II. Intermediate moisture site dominated by Sphagnum spp. (Figure 3) III. Completely thawed wet site dominated by Eriophorum spp. (Figure 4) Sphagnum Average CH4 Exchange by Site mg CH4 m-2 h-1 Net ecosystem exchange (NEE) Respiration Gross Primary Production (GPP) I. Carbon Dioxide Dynamics by Site palsa Examine the dynamics of CO2 Primarily composed of three different ecosystems: RESULTS δ13C-CH4 (‰) Stordalen Mire near Abisko, Sweden (68°21' N, 19°03' E) (Figure 1, shown below) RESEARCH OBJECTIVES mg C m-2h-1 RESEARCH FIELD SITE REFERENCES [1] Callaghan, T. V., F. Bergholm, T. R. Christensen, C. Jonasson, U. Kokfelt, and M. Johansson (2010), A new climate era in the sub-Arctic: Accelerating climate changes and multiple impacts, Geophys. Res. Lett., 37, L14705, doi:10.1029/2009GL042064. [2] Nykänen, H., J. E. P. Heikkinen, L. Pirinen, K. Tiilikainen, and P. J. Martikainen (2003), Annual CO 2 exchange and CH4 fluxes on a subarctic palsa mire during climatically different years, Global Biogeochem. Cycles, 17(1), 1018, doi:10.1029/2002GB001861. [3] Houghton, J. T., Y. Ding, D. J. Griggs, M. Noguer, P. J. van der Winden, and X. Dai (2001), Climate Change 2001: The Scientific Basis. Contri- bution of Working Group 1 to the Third Assessment Report, Cambridge Univ. Press, New York. [4] Bubier, J., T. Moore, K. Savage, and P. Crill (2005), A comparison of methane flux in a boreal landscape between a dry and a wet year, Global Biogeochem. Cycles, 19, GB1023, doi:10.1029/2004GB002351. [5] Joabsson, A., and T. R. Christensen (2001), Methane emissions from wet- lands and their relationship with vascular plants: An Arctic example, Global Change Biol., 7(8), 919–932 [6] Bäckstrand, K., Crill, P. M., Jackowicz-Korczyñski, M., Mastepanov, M., Christensen, T. R., and Bastviken, D. (2009), Annual carbon gas budget for a subarctic peatland, northern Sweden, Biogeosciences Discuss., 6, 5705-5740, doi:10.5194/bgd-6-5705-2009. [6] Whiticar M.J. (1999), Carbon and hydrogen isotope systematics of bacterial formation and oxidation of methane. Chem Geol 161: 291-314. [7] Lansdown J. M., Quay E D. and King S. L. (1992), CH4 production via CO2 reduction in a temperate bog: A source of 13C depleted CH4. GeochimCosmochimActa 56: 3493-3503. [8] Bubier, J. L., T. R. Moore, L. Bellisario, N. T. Comer, and P. M. Crill (1995), Ecological controls on methane emissions from a Northern peatland complex in the zone of discontinuous permafrost, Manitoba, Canada, Global Biogeochem. Cycles, 9(4), 455–470. [9] Updegraff, K. (2001), Response of CO2 and CH4 emissions from peatlands to warming and water table manipulation, Ecol. Appl., 11(2), 311–326.