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Spatial Distribution of Methane in Surface Water from Terrestrial Sources to Coastal Regions Kaitlyn J. Steele Research and Discover 2009 Faculty Advisor: Dr. Ruth K. Varner, EOS
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Greenhouse gases Carbon dioxide concentration in the atmosphere has increased from 280 ppm before the Industrial Revolution to 370 ppm in 2000 Carbon dioxide concentration in the atmosphere has increased from 280 ppm before the Industrial Revolution to 370 ppm in 2000 Methane has increased from 700 ppb to 1,745 ppb Methane has increased from 700 ppb to 1,745 ppb Methane has a global warming potential 23 times greater than CO 2 Methane has a global warming potential 23 times greater than CO 2 MEA 2005
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Role of Oceans The coastal marine ecosystem is attributed with producing 75% of CH 4 emitted by the world’s oceans (Bange et al. 1994) The coastal marine ecosystem is attributed with producing 75% of CH 4 emitted by the world’s oceans (Bange et al. 1994) Ebullition and molecular diffusion are responsible for transport of methane out of sediments (Chanton et al. 1989) Ebullition and molecular diffusion are responsible for transport of methane out of sediments (Chanton et al. 1989) In coastal ecosystems the major pathway for bacterial methane formation is CO 2 reduction by hydrogen In coastal ecosystems the major pathway for bacterial methane formation is CO 2 reduction by hydrogen CO 2 + 4 H 2 → CH 4 + 2 H 2 O 4 H 2 + HCO 3- + H + → CH 4 + 3 H 2 O Methane also produced by acetate fermentation but is limited by sulfate reduction Methane also produced by acetate fermentation but is limited by sulfate reduction CH 3 COOH → CH 4 + CO 2 Whiticar et al. 1986 Hemond and Fechner-Levy 2000
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Objectives Determine the flux of methane produced by anoxic coastal sediments Determine the flux of methane produced by anoxic coastal sediments -Incubation of sediment from tidal flats -Sample surface water of Great Bay estuary Examine the spatial distribution of methane from freshwater to coastal ecosystems Examine the spatial distribution of methane from freshwater to coastal ecosystems -Sample surface of rivers flowing into estuary -Use GIS to identify sources of methane and evaluate transport to coastal regions Methanogenesis: Acetate fermentation Wetlands, WWTP, etc Oxidation, Diffusive Flux, Advective Transport Estuary, saltmarsh Methanogenesis: CO 2 Reduction Oxidation, Air-Sea Exchange
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Methods Incubations Sediment core taken in Great Bay Estuary at tidal flats Sediment core taken in Great Bay Estuary at tidal flats 10-20 g of sediment from 0-5, 5-10, 10-15 and 15-20 cm incubated under anaerobic conditions 10-20 g of sediment from 0-5, 5-10, 10-15 and 15-20 cm incubated under anaerobic conditions 10 mL of headspace sampled daily and analyzed for CH 4 concentration using GC-FID 10 mL of headspace sampled daily and analyzed for CH 4 concentration using GC-FID Water Sampling Surface water collected in container and syringe used to sample 30 mL of water Surface water collected in container and syringe used to sample 30 mL of water 30 mL of ambient air drawn in and syringe shaken to flush dissolved methane into the headspace 30 mL of ambient air drawn in and syringe shaken to flush dissolved methane into the headspace Headspace injected into GC-FID to obtain CH 4 concentration Headspace injected into GC-FID to obtain CH 4 concentration
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Methane Concentration in Surface Water
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Methane Concentration in Rivers 2008 2009 Examples of Sources: Sallie’s Fen 4805 ppmv Durham Wastewater Treatment Plant 44 ppmv
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Difference in CH 4 Concentration from 2008 to 2009
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Methane Flux from Rivers to Atmosphere 2008 2009
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Soil Incubations Depth (cm) Moisture Content (%) Organic Matter (%) Average Flux (mg CH 4 /g sed*day) 538.9 ± 1.25.0 ± 0.50.98 ± 0.12 1033.6 ± 1.84.5 ± 1.01.59 ± 0.77 1532.0 ± 0.85.3 ± 0.72.67 ± 0.68 2029.2 ± 0.44.3 ± 0.513.48 ± 13.05
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Future Work Methane produced through CO 2 reduction is isotopically light with δ 13 C values between -110 and -60‰ Methane produced through CO 2 reduction is isotopically light with δ 13 C values between -110 and -60‰ CH 4 produced by acetate fermentation has δ 13 C values between -65 and -50‰ CH 4 produced by acetate fermentation has δ 13 C values between -65 and -50‰ Methane oxidation converts some of the methane produced at depth to carbon dioxide as it rises to a level where oxygen is present Methane oxidation converts some of the methane produced at depth to carbon dioxide as it rises to a level where oxygen is present Since the 13 C/ 12 C ratios of dissolved CO 2 are affected by the equilibria of many kinetic isotope effects it is necessary to calculate the carbon isotopic fractionation between methane and carbon dioxide Since the 13 C/ 12 C ratios of dissolved CO 2 are affected by the equilibria of many kinetic isotope effects it is necessary to calculate the carbon isotopic fractionation between methane and carbon dioxide Whiticar et al. 1986
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NASA Relevance Evaluating sources of methane can aid in determining processes that produce atmospheric methane Evaluating sources of methane can aid in determining processes that produce atmospheric methane TDL spectroscopy from aircraft TDL spectroscopy from aircraft Remote sensing using AIRS instrument on AQUA satellite Remote sensing using AIRS instrument on AQUA satellite AIRS CH 4 at 300hPa
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Acknowledgements Dr. Ruth Varner Dr. George Hurtt Olivia DeMeo Jordan Goodrich NASA/UNH R&D
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References Bange, H.W., U.H. Bartell, S. Rapsomanikis and M.O. Andreae. 1994. Methane in the Baltic Sea and North Seas and a reassessment of the marine emissions of methane. Global Biogeochem. Cycles 8: 465– 480. Bange, H.W., U.H. Bartell, S. Rapsomanikis and M.O. Andreae. 1994. Methane in the Baltic Sea and North Seas and a reassessment of the marine emissions of methane. Global Biogeochem. Cycles 8: 465– 480. Capone, D.G. and R.P. Kiene. 1988. Comparison of microbial dynamics in marine and freshwater sediments: contrasts in anaerobic carbon catabolism. Limnology and Oceanography. 33: 725-749. Capone, D.G. and R.P. Kiene. 1988. Comparison of microbial dynamics in marine and freshwater sediments: contrasts in anaerobic carbon catabolism. Limnology and Oceanography. 33: 725-749. Chanton, J.P., C.S. Martens, C.A. Kelley. 1989. Gas transport from methane-saturated, tidal freshwater and wetland sediments. Limnology and Oceanography. 34: 807-819. Chanton, J.P., C.S. Martens, C.A. Kelley. 1989. Gas transport from methane-saturated, tidal freshwater and wetland sediments. Limnology and Oceanography. 34: 807-819. Crill, P.M. and C. S. Martens. 1986. Methane production from bicarbonate and acetate in anoxic marine sediment. Geochimica et Cosmochimica Act. 50: 2089-2097. Crill, P.M. and C. S. Martens. 1986. Methane production from bicarbonate and acetate in anoxic marine sediment. Geochimica et Cosmochimica Act. 50: 2089-2097. Millennium Ecosystem Assessment. 2005. Ecosystems and Human Well-Being: Current States and Trends, Volume 1. Island Press, Washington. Millennium Ecosystem Assessment. 2005. Ecosystems and Human Well-Being: Current States and Trends, Volume 1. Island Press, Washington. Webster, C.R. 2005. Measuring methane and its isotopes 12CH4, 13CH4,and CH3D on the surface of Mars with in situ laserspectroscopy. Applied Optics. 44: 1226-1235. Webster, C.R. 2005. Measuring methane and its isotopes 12CH4, 13CH4,and CH3D on the surface of Mars with in situ laserspectroscopy. Applied Optics. 44: 1226-1235. Whiticar, M.J., E. Farber, and M. Schoell. 1986. Biogenic methane formation in marine and freshwater environments: CO2 reduction vs. acetate fermentation-Isotopic evidence. Geochimica et Cosmochimica Act. 50: 693-709. Whiticar, M.J., E. Farber, and M. Schoell. 1986. Biogenic methane formation in marine and freshwater environments: CO2 reduction vs. acetate fermentation-Isotopic evidence. Geochimica et Cosmochimica Act. 50: 693-709. Whiticar, M. and H. Schaefer. 2007. Constraining past tropospheric methane budgets with carbon and hydrogen isotope ratios in ice. Phil. Trans. R. Soc. A. 365: 1793-1828. Whiticar, M. and H. Schaefer. 2007. Constraining past tropospheric methane budgets with carbon and hydrogen isotope ratios in ice. Phil. Trans. R. Soc. A. 365: 1793-1828. Winfrey, M.R., D.R. Nelson, S.C. Klevickis and J.G. Zeikus. 1977. Association of hydrogen metabolism with methanogenesis in lake Mendota sediments. Appl. Environ. Microbiol. 33: 312–318. Winfrey, M.R., D.R. Nelson, S.C. Klevickis and J.G. Zeikus. 1977. Association of hydrogen metabolism with methanogenesis in lake Mendota sediments. Appl. Environ. Microbiol. 33: 312–318. Wingenter, O.W. 2007. Unexpected consequences of increasing CO2 and ocean acidity on marine production of DMS and CH2ClI: Potential climate impacts. Geophysical Research Letters 34. Wingenter, O.W. 2007. Unexpected consequences of increasing CO2 and ocean acidity on marine production of DMS and CH2ClI: Potential climate impacts. Geophysical Research Letters 34.
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