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by admin | Apr 15, 2019 | vol10 | 0 comments

J.L. Ash, M. Egger, T. Treude, I. Kohl, B. Cragg, R.J. Parkes, C.P. Slomp, B. Sherwood Lollar, E.D. Young

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Exchange catalysis during anaerobic methanotrophy revealed by 12CH2D2 and 13CH3D in methane

J.L. Ash1,

1Department of Earth, Environmental and Planetary Sciences, Rice University, Houston Texas, USA

M. Egger2,#,

2Center for Geomicrobiology, Aarhus University, Aarhus, Denmark
#now at The Ocean Cleanup Foundation, Rotterdam, The Netherlands

T. Treude3,4,

3Department of Earth, Planetary, and Space Sciences, UCLA, Los Angeles CA, USA
4School of Earth and Ocean Sciences, Cardiff University, Cardiff, UK

I. Kohl3,

3Department of Earth, Planetary, and Space Sciences, UCLA, Los Angeles CA, USA

B. Cragg4,

4School of Earth and Ocean Sciences, Cardiff University, Cardiff, UK

R.J. Parkes4,

4School of Earth and Ocean Sciences, Cardiff University, Cardiff, UK

C.P. Slomp5,

5Department of Earth Sciences-Geochemistry, Utrecht University, Utrecht, The Netherlands

B. Sherwood Lollar6,

6Department of Earth Sciences, University of Toronto, Toronto Ontario, Canada

E.D. Young3

3Department of Earth, Planetary, and Space Sciences, UCLA, Los Angeles CA, USA

Affiliations  |  Corresponding Author  |  Cite as  |  Funding information

J.L. Ash, E.D. Young
Email: jeanine.ash@rice.edu; eyoung@epss.ucla.edu

1Department of Earth, Environmental and Planetary Sciences, Rice University, Houston Texas, USA
2Center for Geomicrobiology, Aarhus University, Aarhus, Denmark
3Department of Earth, Planetary, and Space Sciences, UCLA, Los Angeles CA, USA
4School of Earth and Ocean Sciences, Cardiff University, Cardiff, UK
5Department of Earth Sciences-Geochemistry, Utrecht University, Utrecht, The Netherlands
6Department of Earth Sciences, University of Toronto, Toronto Ontario, Canada
#now at The Ocean Cleanup Foundation, Rotterdam, The Netherlands

Ash, J.L., Egger, M., Treude, T., Kohl, I., Cragg, B., Parkes, R.J., Slomp, C.P., Sherwood Lollar, B., Young, E.D. (2019) Exchange catalysis during anaerobic methanotrophy revealed by 12CH2D2 and 13CH3D in methane. Geochem. Persp. Let. 10, 26–30.

The Deep Carbon Observatory

Geochemical Perspectives Letters v10  |  doi: 10.7185/geochemlet.1910
Received 07 May 2018  |  Accepted 22 February 2019  |  Published 15 April 2019

Copyright © The Authors

Published by the European Association of Geochemistry
under Creative Commons License CC BY-NC-ND 4.0

 

Keywords: methane, clumped isotopes, anaerobic methanotrophy, deep biosphere, Integrated Ocean Drilling Program Exp. 347

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Abstract

Abstract | Letter | Acknowledgements | References | Supplementary Information

The anaerobic oxidation of methane (AOM) is a crucial component of the methane cycle, but quantifying its role in situ under dynamic environmental conditions remains challenging. We use sediment samples collected during IODP Expedition 347 to the Baltic Sea to show that relative abundances of 12CH2D2 and 13CH3D in methane remaining after microbial oxidation are in internal, thermodynamic isotopic equilibrium, and we attribute this phenomenon to the reversibility of the initial step of AOM. These data suggest that 12CH2D2 and 13CH3D together can identify the influence of anaerobic methanotrophy in environments where conventional bulk isotope ratios are ambiguous, and these findings may lead to new insights regarding the global significance of enzymatic back reaction in the methane cycle.

Figures and Tables

Figure 1 Geochemical profiles (±2 σ) from Bornholm Basin from 3-35 MCD. Horizontal grey bar denotes sediments deposited during lacustrine conditions overlain with sediments deposited during brackish marine conditions. Samples were not recovered above the shallow SMTZ. Pink dashed lines denote a shallow (3.3 MCD) and deep (19.8 MCD) SMTZ; only the shallow SMTZ is shown in the bottom panel for clarity. Dark grey vertical bars in e and f denote equilibrium isotopologue compositions for the subsurface temperature of 7.8 ± 0.6 °C. Modelled CH4 production, Fe-AOM and SO4-AOM rates are shown in panel d (Dijkstra et al., 2018). CH4 production (purple) and SO4-AOM (gold) rates correspond with the upper x axis and Fe-AOM rates (brown) correspond with the lower x axis. SO4-AOM rates above the upper SMTZ are calculated using bottom water SO4 concentrations of 15.0 mM. Additional porewater data shown in Supplementary Information.

Figure 2 ξ12CH2D2 values (±2 σ) are the most negative at shallow MCD, indicating the greatest departure from equilibrium and approach zero (violet dashed line) with increasing MCD, indicating an approach towards intra-species thermodynamic equilibrium. ΔG values for SO4-AOM and Fe-AOM suggest either metabolism is capable of reversibility (see Supplementary Information).

Figure 3 Δ12CH2D2 is plotted versus Δ13CH3D. The solid black line represents theoretical thermodynamic equilibrium abundances (with dots representing 100 °C increments from 0-1000 °C). Methane produced by thermogenesis, high temperature abiotic reactions, microbial methanogenesis and low temperature abiotic reactions inhabit unique zones in double isotopologue space. AOM, equilibrating through exchange catalysis during enzymatic back reaction, also inhibits a unique zone: low temperature intra-species thermodynamic equilibrium. Bornholm Basin data (magenta diamonds) span between the methanogenesis and AOM zones, while data from Kidd Creek Mine (black to white symbols) (Young et al., 2017) span from the abiotic to AOM zone. See Supplementary Information for additional sample description.

Figure 1Figure 2Figure 3

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Letter

Abstract | Letter | Acknowledgements | References | Supplementary Information

Quantifying the subsurface carbon cycle by linking biogeochemistry to deep biosphere metabolisms remains a long-standing challenge compounded by slow rates of reaction (Edwards et al., 2012

Edwards, K.J., Becker, K., Colwell, F. (2012) The deep, dark energy biosphere: intraterrestrial life on earth. Annual Review of Earth and Planetary Sciences 40, 551-568.

; Marlow et al., 2017

Marlow, J.J., Steele, J.A., Ziebis, W., Sheller, S., Case, D., Reynard, L.M., Orphan, V.J. (2017) Monodeuterated Methane, an Isotopic Tool To Assess Biological Metabolism Rates. mSphere 2, e00309-17.

). Even in well-characterised environments, determining how methanogens and anaerobic methanotrophs influence organic matter degradation can be challenging (Regnier et al., 2011

Regnier, P., Dale, A.W., Arndt, S., LaRowe, D., Mogollón, J., Van Cappellen, P. (2011) Quantitative analysis of anaerobic oxidation of methane (AOM) in marine sediments: a modeling perspective. Earth-Science Reviews 106, 105-130.

; Beulig et al., 2018

Beulig, F., Røy, H., Glombitza, C., Jørgensen, B. (2018) Control on rate and pathway of anaerobic organic carbon degradation in the seabed. Proceedings of the National Academy of Sciences 115, 367-372.

). These challenges are due in part to how methane produced by methanogens inherits characteristics from its substrates (both a range of organic and inorganic carbon) (Conrad, 2005

Conrad, R. (2005) Quantification of methanogenic pathways using stable carbon isotopic signatures: a review and a proposal. Organic Geochemistry 36, 739-752.

), and they are further complicated when methane is itself the substrate during anaerobic methane oxidation (AOM) (Whiticar, 1999

Whiticar, M.J. (1999) Carbon and hydrogen isotope systematics of bacterial formation and oxidation of methane. Chemical Geology 161, 291-314.

).  Our understanding of how anaerobic methanotrophs respond to varying environmental conditions (Holler et al., 2009

Holler, T., Wegener, G., Knittel, K., Boetius, A., Brunner, B., Kuypers, M.M., Widdel, F. (2009) Substantial 13C/12C and D/H fractionation during anaerobic oxidation of methane by marine consortia enriched in vitro. Environmental Microbiology Reports 1, 370-376.

, 2011

Holler, T., Wegener, G., Niemann, H., Deusner, C., Ferdelman, T.G., Boetius, A., Brunner, B., Widdel, F. (2011) Carbon and sulfur back flux during anaerobic microbial oxidation of methane and coupled sulfate reduction. Proceedings of the National Academy of Sciences 108, E1484-E1490.

; Yoshinaga et al., 2014

Yoshinaga, M.Y., Holler, T., Goldhammer, T., Wegener, G., Pohlman, J.W., Brunner, B., Kuypers, M.M.M., Hinrichs, K.U., Elvert, M. (2014) Carbon isotope equilibration during sulphate-limited anaerobic oxidation of methane. Nature Geoscience 7, 190-194.

) and how they might contribute to “cryptic cycles” (the rapid production and consumption of reactive intermediates) in the marine subsurface is constantly evolving (Egger et al., 2018

Egger, M., Riedinger, N., Mogollón, J.M., Jørgensen, B.B. (2018) Global diffusive fluxes of methane in marine sediments. Nature Geoscience 11, 421.

).

AOM is thought to be carried out by a consortium of methane oxidising archaea and sulphate reducing bacteria performing the net reaction CH4 + SO32- → HCO3- + HS- + H2O (Boetius et al., 2000

Boetius, A., Ravenschlag, K., Schubert, C.J., Rickert, D., Widdel, F., Gieseke, A., Amann, R., Jørgensen, B.B., Witte, U., Pfannkuche, O. (2000) A marine microbial consortium apparently mediating anaerobic oxidation of methane. Nature 407, 623-626.

). Evidence suggests that these processes can be decoupled (Milucka et al., 2012

Milucka, J., Ferdelman, T.G., Polerecky, L., Franzke, D., Wegener, G., Schmid, M., Lieberwirth, I., Wagner, M., Widdel, F., Kuypers, M.M. (2012) Zero-valent sulphur is a key intermediate in marine methane oxidation. Nature 491, 541-546.

; Scheller et al., 2016

Scheller, S., Yu, H., Chadwick, G.L., McGlynn, S.E., Orphan, V.J. (2016) Artificial electron acceptors decouple archaeal methane oxidation from sulfate reduction. Science 351, 703-707.

) and metal oxides may also act as terminal electron acceptors (Beal et al., 2009

Beal, E.J., House, C.H., Orphan, V.J. (2009) Manganese-and iron-dependent marine methane oxidation. Science 325, 184-187.

; Cai et al., 2018

Cai, C., Leu, A.O., Xie, G.-J., Guo, J., Feng, Y., Zhao, J.-X., Tyson, G.W., Yuan, Z., Hu, S. (2018) A methanotrophic archaeon couples anaerobic oxidation of methane to Fe (III) reduction. The ISME Journal 12, 1929-1939.

). In all cases, the first step of AOM involves C-H bond activation by a modified methyl-coenzyme M reductase (Mcr), the terminal enzyme in methanogenesis (Scheller et al., 2010

Scheller, S., Goenrich, M., Boecher, R., Thauer, R.K., Jaun, B. (2010) The key nickel enzyme of methanogenesis catalyses the anaerobic oxidation of methane. Nature 465, 606.

). Anaerobic methanotrophs use enzymes homologous to those used by methanogens (Krüger et al., 2003

Krüger, M., Meyerdierks, A., Glöckner, F.O., Amann, R., Widdel, F., Kube, M., Reinhardt, R., Kahnt, J., Böcher, R., Thauer, R.K. (2003) A conspicuous nickel protein in microbial mats that oxidize methane anaerobically. Nature 426, 878-881.

; Shima et al., 2012

Shima, S., Krueger, M., Weinert, T., Demmer, U., Kahnt, J., Thauer, R.K., Ermler, U. (2012) Structure of a methyl-coenzyme M reductase from Black Sea mats that oxidize methane anaerobically. Nature 481, 98.

), prompting questions regarding the directionality of these metabolisms (Lloyd et al., 2011

Lloyd, K.G., Alperin, M.J., Teske, A. (2011) Environmental evidence for net methane production and oxidation in putative ANaerobic MEthanotrophic (ANME) archaea. Environmental Microbiology 13, 2548-2564.

; Beulig et al., 2019

Beulig, F., Røy, H., McGlynn, S., Jørgensen, B. (2019) Cryptic CH4 cycling in the sulfate-methane transition of marine sediments apparently mediated by ANME-1 archaea. The ISME Journal 13, 250-262.

).

Coupling exploration of methane enzymatic chemistry with isotope geochemistry can provide powerful insights. Here, we interrogate subsurface methane metabolisms by precisely determining concentrations of molecules containing two heavy isotopes, referred to as “clumped” isotopologues (Eiler, 2007

Eiler, J.M. (2007) "Clumped-isotope" geochemistry -- The study of naturally-occurring, multiply-substituted isotopologues. Earth and Planetary Science Letters 262, 309-327.

). The relative proportions of 13CH3D and 12CH2D2 (reported as Δ13CH3D and Δ12CH2D2 values relative to a random distribution of isotopes among all CH4 isotopologues; see Supplementary Information) have known temperature sensitive equilibrium concentrations and thus are sensitive indicators of reversibility in reactions (Piasecki et al., 2016

Piasecki, A., Sessions, A., Peterson, B., Eiler, J. (2016) Prediction of equilibrium distributions of isotopologues for methane, ethane and propane using density functional theory. Geochimica et Cosmochimica Acta 190, 1-12.

).  For instance, axenic cultures of methanogens produce methane with depletions in clumped isotopes relative to the random distribution that reflect kinetic processes (Stolper et al., 2015

Stolper, D.A., Martini, A.M., Clog, M., Douglas, P.M., Shusta, S.S., Valentine, D.L., Sessions, A.L., Eiler, J.M. (2015) Distinguishing and understanding thermogenic and biogenic sources of methane using multiply substituted isotopologues. Geochimica et Cosmochimica Acta 161, 219-247.

; Wang et al., 2015

Wang, D.T., Gruen, D.S., Lollar, B.S., Hinrichs, K.-U., Stewart, L.C., Holden, J.F., Hristov, A.N., Pohlman, J.W., Morrill, P.L., Könneke, M. (2015) Nonequilibrium clumped isotope signals in microbial methane. Science 348, 428-431.

; Douglas et al., 2016

Douglas, P., Stolper, D., Smith, D., Anthony, K.W., Paull, C., Dallimore, S., Wik, M., Crill, P.M., Winterdahl, M., Eiler, J. (2016) Diverse origins of Arctic and Subarctic methane point source emissions identified with multiply-substituted isotopologues. Geochimica et Cosmochimica Acta 188, 163-188.

; Young et al., 2017

Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.

; Gruen et al., 2018

Gruen, D.S., Wang, D.T., Könneke, M., Topçuoğlu, B.D., Stewart, L.C., Goldhammer, T., Holden, J.F., Hinrichs, K.-U., Ono, S. (2018) Experimental investigation on the controls of clumped isotopologue and hydrogen isotope ratios in microbial methane. Geochimica et Cosmochimica Acta 237, 339-356.

). In some cases, the clumped isotope composition of environmental microbial methane is consistent with the axenic cultures, but in others it displays a clumped isotope composition reflective of equilibration within the environment of formation (Wang et al., 2015

Wang, D.T., Gruen, D.S., Lollar, B.S., Hinrichs, K.-U., Stewart, L.C., Holden, J.F., Hristov, A.N., Pohlman, J.W., Morrill, P.L., Könneke, M. (2015) Nonequilibrium clumped isotope signals in microbial methane. Science 348, 428-431.

; Young et al., 2017

Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.

). This span in clumped isotope distributions suggests that enzymatic reactions associated with methanogenesis and methanotrophy are capable of ranging from reversible to kinetic. Previous work using one rare isotopologue (Δ13CH3D) suggests that the rate of methanogenesis controls the degree of molecular isotopic equilibrium (Stolper et al., 2015

Stolper, D.A., Martini, A.M., Clog, M., Douglas, P.M., Shusta, S.S., Valentine, D.L., Sessions, A.L., Eiler, J.M. (2015) Distinguishing and understanding thermogenic and biogenic sources of methane using multiply substituted isotopologues. Geochimica et Cosmochimica Acta 161, 219-247.

; Wang et al., 2015

Wang, D.T., Gruen, D.S., Lollar, B.S., Hinrichs, K.-U., Stewart, L.C., Holden, J.F., Hristov, A.N., Pohlman, J.W., Morrill, P.L., Könneke, M. (2015) Nonequilibrium clumped isotope signals in microbial methane. Science 348, 428-431.

). However, the inability to produce equilibrated methane from axenic cultures has led to speculation that AOM may be responsible for equilibrated environmental methane (Stolper et al., 2015

Stolper, D.A., Martini, A.M., Clog, M., Douglas, P.M., Shusta, S.S., Valentine, D.L., Sessions, A.L., Eiler, J.M. (2015) Distinguishing and understanding thermogenic and biogenic sources of methane using multiply substituted isotopologues. Geochimica et Cosmochimica Acta 161, 219-247.

; Wang et al., 2016

Wang, D.T., Welander, P.V., Ono, S. (2016) Fractionation of the methane isotopologues 13 CH 4, 12 CH 3 D, and 13 CH 3 D during aerobic oxidation of methane by Methylococcus capsulatus (Bath). Geochimica et Cosmochimica Acta 192, 186-202.

; Young et al., 2017

Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.

; Gruen et al., 2018

Gruen, D.S., Wang, D.T., Könneke, M., Topçuoğlu, B.D., Stewart, L.C., Goldhammer, T., Holden, J.F., Hinrichs, K.-U., Ono, S. (2018) Experimental investigation on the controls of clumped isotopologue and hydrogen isotope ratios in microbial methane. Geochimica et Cosmochimica Acta 237, 339-356.

).  The use of a second rare isotopologue, 12CH2D2, aids in interpreting the causes of intra-methane disequilibrium and suggests that microbial methanogenesis does not lead to isotopologue equilibrium among methane molecules.

Here, we examine microbial methane from the Bornholm Basin (Baltic Sea; see Supplementary Information) to test the hypothesis that methane remaining after anaerobic oxidation is in thermodynamic equilibrium due to reversibility of the initial step of AOM. We compare methane clumped isotope composition to geochemical profiles (Andrén et al., 2015

Andrén, T., Jorgensen, B., Cotterill, C., Green, S., Andrén, E., Ash, J., Bauersachs, T., Cragg, B., Fanget, A., Fehr, A. (2015) Expedition 347 Baltic Sea Paleoenvironment. Proceedings of the Integrated Ocean Drilling Program 347, 1-66.

; Egger et al., 2017

Egger, M., Hagens, M., Sapart, C.J., Dijkstra, N., van Helmond, N.A., Mogollón, J.M., Risgaard-Petersen, N., van der Veen, C., Kasten, S., Riedinger, N. (2017) Iron oxide reduction in methane-rich deep Baltic Sea sediments. Geochimica et Cosmochimica Acta 207, 256-276.

) and present day rates of methanogenesis and methanotrophy calculated with a multicomponent diagenetic model (Dijkstra et al., 2018

Dijkstra, N., Hagens, M., Egger, M., Slomp, C.P. (2018) Post-depositional vivianite formation alters sediment phosphorus records. Biogeosciences 15, 861-883.

) to determine parameters controlling the isotopic composition of methane (Fig. 1a-d). Methane δ13C and δD, δ13CDIC, δ13CTOC and δDH2O vary non-monotonically over 30 metres below seafloor (Fig. 1g,h; Fig. S-1) while Δ13CH3D and Δ12CH2D2 values increase with depth (Fig. 1e,f).


Figure 1 Geochemical profiles (±2 σ) from Bornholm Basin from 3-35 MCD. Horizontal grey bar denotes sediments deposited during lacustrine conditions overlain with sediments deposited during brackish marine conditions. Samples were not recovered above the shallow SMTZ. Pink dashed lines denote a shallow (3.3 MCD) and deep (19.8 MCD) SMTZ; only the shallow SMTZ is shown in the bottom panel for clarity. Dark grey vertical bars in e and f denote equilibrium isotopologue compositions for the subsurface temperature of 7.8 ± 0.6 °C. Modelled CH4 production, Fe-AOM and SO4-AOM rates are shown in panel d (Dijkstra et al., 2018

Dijkstra, N., Hagens, M., Egger, M., Slomp, C.P. (2018) Post-depositional vivianite formation alters sediment phosphorus records. Biogeosciences 15, 861-883.

). CH4 production (purple) and SO4-AOM (gold) rates correspond with the upper x axis and Fe-AOM rates (brown) correspond with the lower x axis. SO4-AOM rates above the upper SMTZ are calculated using bottom water SO4 concentrations of 15.0 mM. Additional porewater data shown in Supplementary Information.
Full size image | Download in Powerpoint

Comparisons of the bulk isotopic composition of methane to carbon and hydrogen reservoirs at this location are complicated by the change from limnic to marine deposition (Egger et al., 2017

Egger, M., Hagens, M., Sapart, C.J., Dijkstra, N., van Helmond, N.A., Mogollón, J.M., Risgaard-Petersen, N., van der Veen, C., Kasten, S., Riedinger, N. (2017) Iron oxide reduction in methane-rich deep Baltic Sea sediments. Geochimica et Cosmochimica Acta 207, 256-276.

).  For instance, the hydrogen isotopes in methane are seemingly not equilibrated with porewater that changes by >100 ‰ in this interval (Fig. S-1), obscuring the history of this reservoir.  Instead, we will focus on the intra-molecular isotopic equilibrium of the methane itself using clumped isotopes, thus sidestepping the complications in bulk isotope ratios.  We introduce ξ12CH2D2, a parameter that quantifies the degree of thermodynamic disequilibrium for a methane system. ξ12CH2D2 is analogous to the symbol for the reaction progress variable (ξ12CH2D2 = Δ12CH2D2, measured - Δ12CH2D2, equilibrium, see Supplementary Information). Values for ξ12CH2D2 in upper sediments as low as -7.5 ‰ are significantly different (>6 σ) from 0 ‰ (i.e. thermodynamic equilibrium) which is approached with depth (Fig. 2). In order to determine how methanogenesis and methanotrophy influence this transition, we consider evidence for and against reversibility in each metabolism.


Figure 2 ξ12CH2D2 values (±2 σ) are the most negative at shallow MCD, indicating the greatest departure from equilibrium and approach zero (violet dashed line) with increasing MCD, indicating an approach towards intra-species thermodynamic equilibrium. ΔG values for SO4-AOM and Fe-AOM suggest either metabolism is capable of reversibility (see Supplementary Information).
Full size image | Download in Powerpoint

Methanogenesis in intra-molecular isotopic thermodynamic equilibrium requires reversibility at the final hydrogen addition step. Trace methane oxidation (TMO) does occur during methanogenesis, but altering the concentration of H2 or terminal electron acceptors necessary for oxidising methane does not increase TMO and has never been shown to consume greater than ~3 % of the CH4 produced (Moran et al., 2005

Moran, J.J., House, C.H., Freeman, K.H., Ferry, J.G. (2005) Trace methane oxidation studied in several Euryarchaeota under diverse conditions. Archaea 1, 303-309.

; Moran et al., 2007

Moran, J.J., House, C.H., Thomas, B., Freeman, K.H. (2007) Products of trace methane oxidation during nonmethyltrophic growth by Methanosarcina. Journal of Geophysical Research: Biogeosciences 112.

). Although some of the first steps of methanogenesis may be reversible (Valentine et al., 2004

Valentine, D.L., Chidthaisong, A., Rice, A., Reeburgh, W.S., Tyler, S.C. (2004) Carbon and hydrogen isotope fractionation by moderately thermophilic methanogens. Geochimica et Cosmochimica Acta 68, 1571-1590.

), the final transfer of the methyl group to coenzyme M and the subsequent final hydrogen addition are believed to be irreversible (Gärtner et al., 1994

Gärtner, P., Weiss, D.S., Harms, U., Thauer, R.K. (1994) N5‐Methyltetrahydromethanopterin: Coenzyme M Methyltransferase from Methanobacterium thermoautotrophicum. The FEBS Journal 226, 465-472.

; Thauer, 2011

Thauer, R.K. (2011) Anaerobic oxidation of methane with sulfate: on the reversibility of the reactions that are catalyzed by enzymes also involved in methanogenesis from CO2. Current Opinion in Microbiology 14, 292-299.

).  Work on determining the biochemical pathways of Fe(III) reducing ANME has so far required genetically modifying a methanogen, M. acetivorans with the Mcr from an ANME-1 group organism because unmodified M. acetivorans are unable to be cultured on methane without the modified Mcr (Soo et al., 2016

Soo, V.W., McAnulty, M.J., Tripathi, A., Zhu, F., Zhang, L., Hatzakis, E., Smith, P.B., Agrawal, S., Nazem-Bokaee, H., Gopalakrishnan, S. (2016) Reversing methanogenesis to capture methane for liquid biofuel precursors. Microbial cell factories 15, 11.

; Yan et al., 2018

Yan, Z., Joshi, P., Gorski, C.A., Ferry, J.G. (2018) A biochemical framework for anaerobic oxidation of methane driven by Fe (III)-dependent respiration. Nature Communications 9.

).

In contrast, AOM is known to have an enzymatic back reaction that suggests the first step of anaerobic methanotrophy is partially reversible, providing a potential mechanism for equilibrating methane isotopologues with environmental temperatures.  This back reaction is sensitive to concentrations of the terminal electron acceptor SO42- (Holler et al., 2011

Holler, T., Wegener, G., Niemann, H., Deusner, C., Ferdelman, T.G., Boetius, A., Brunner, B., Widdel, F. (2011) Carbon and sulfur back flux during anaerobic microbial oxidation of methane and coupled sulfate reduction. Proceedings of the National Academy of Sciences 108, E1484-E1490.

; Yoshinaga et al., 2014

Yoshinaga, M.Y., Holler, T., Goldhammer, T., Wegener, G., Pohlman, J.W., Brunner, B., Kuypers, M.M.M., Hinrichs, K.U., Elvert, M. (2014) Carbon isotope equilibration during sulphate-limited anaerobic oxidation of methane. Nature Geoscience 7, 190-194.

).  At high concentrations of SO42-, the back reaction produces 3-7 % of the CH4 consumed by AOM, and at low concentrations of SO42- (below 0.5 mM), back reaction can produce as much as 78 % of the CH4 consumed by AOM (Yoshinaga et al., 2014

Yoshinaga, M.Y., Holler, T., Goldhammer, T., Wegener, G., Pohlman, J.W., Brunner, B., Kuypers, M.M.M., Hinrichs, K.U., Elvert, M. (2014) Carbon isotope equilibration during sulphate-limited anaerobic oxidation of methane. Nature Geoscience 7, 190-194.

; Timmers et al., 2017

Timmers, P.H., Welte, C.U., Koehorst, J.J., Plugge, C.M., Jetten, M.S., Stams, A.J. (2017) Reverse Methanogenesis and respiration in methanotrophic archaea. Archaea 2017.

). Intra-cellular exposure of methane to Mcr can lead to isotope exchange catalysis during bond rupture and reformation (Marlow et al., 2017

Marlow, J.J., Steele, J.A., Ziebis, W., Sheller, S., Case, D., Reynard, L.M., Orphan, V.J. (2017) Monodeuterated Methane, an Isotopic Tool To Assess Biological Metabolism Rates. mSphere 2, e00309-17.

), and methane that diffuses back out of the cell could move an environmental reservoir of methane towards thermodynamic equilibrium. Using estimates of AOM rates from Dijkstra et al. (2018)

Dijkstra, N., Hagens, M., Egger, M., Slomp, C.P. (2018) Post-depositional vivianite formation alters sediment phosphorus records. Biogeosciences 15, 861-883.

, we calculate the timescale of this equilibration (see Supplementary Information) to be on the order of 103-104 years, consistent with the estimated age of methane at 20 MCD of <~8000 years (Figs. S-1, S-2).  Such timescales would vary in environments with differing rates of AOM.

Our findings suggest that when terminal electron acceptors are limiting, equilibrium bond ordering may be used to identify AOM activity even when the bulk isotopic composition of reservoir material is changing and ambiguous. Methane from Kidd Creek Mine (Ontario, Canada) also shows methane isotopologues transitioning with time from non-equilibrated to equilibrated (Fig. 3).  This suggests that as energy-rich fractures open, Mcr exposure during the initial step of AOM catalytically exchanges isotopes leaving behind a reservoir that moves closer to thermodynamic equilibrium (Young et al., 2017

Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.

).


Figure 3 Δ12CH2D2 is plotted versus Δ13CH3D. The solid black line represents theoretical thermodynamic equilibrium abundances (with dots representing 100 °C increments from 0-1000 °C). Methane produced by thermogenesis, high temperature abiotic reactions, microbial methanogenesis and low temperature abiotic reactions inhabit unique zones in double isotopologue space. AOM, equilibrating through exchange catalysis during enzymatic back reaction, also inhibits a unique zone: low temperature intra-species thermodynamic equilibrium. Bornholm Basin data (magenta diamonds) span between the methanogenesis and AOM zones, while data from Kidd Creek Mine (black to white symbols) (Young et al., 2017

Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.

) span from the abiotic to AOM zone. See Supplementary Information for additional sample description.
Full size image | Download in Powerpoint

Methane remaining after AOM is in low temperature equilibrium due to exchange catalysis by Mcr.  Therefore, it has distinct Δ13CH3D and Δ12CH2D2 concentrations when compared to methane produced through other known mechanisms (thermogenesis, microbial methanogenesis and abiotic methanogenesis) (Fig. 3).  AOM metabolisms have been shown to be active from -1 °C to 70 °C (Niemann et al., 2006

Niemann, H., Lösekann, T., De Beer, D., Elvert, M., Nadalig, T., Knittel, K., Amann, R., Sauter, E.J., Schlüter, M., Klages, M. (2006) Novel microbial communities of the Haakon Mosby mud volcano and their role as a methane sink. Nature 443, 854-858.

; Holler et al., 2011

Holler, T., Wegener, G., Niemann, H., Deusner, C., Ferdelman, T.G., Boetius, A., Brunner, B., Widdel, F. (2011) Carbon and sulfur back flux during anaerobic microbial oxidation of methane and coupled sulfate reduction. Proceedings of the National Academy of Sciences 108, E1484-E1490.

), a range of temperatures that is unique and distinguishable from equilibrated thermogenic methane forming in the 100 °C to 250 °C gas window. Abiotic methane may also form at low temperatures, yet even when it is apparently equilibrated in Δ13CH3D, it may exhibit large depletions in Δ12CH2D2 that distinguish it from methane that has undergone exchange catalysis during AOM.  We suggest that when combined (as in the ξ12CH2D2 parameter), Δ12CH2D2 and Δ13CH3D values are sensitive indicators of the degree of thermodynamic equilibrium that may be useful in determining the role of enzymatic back reaction during AOM in the global methane cycle.

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Acknowledgements

Abstract | Letter | Acknowledgements | References | Supplementary Information

We thank five anonymous reviewers for helpful critiques as well as Laurence Yeung and Edwin Schauble for conversations and advice on early versions of this manuscript. JLA was funded by an NSF GRFP (DGE – 1144087) while this work was ongoing.  We thank the crew and technical staff of the Greatship Manisha.  This research used samples and/or data provided by the International Ocean Discovery Program (IODP). Funding for this research was provided to JLA and TT by the Deep Carbon Observatory’s Deep Energy Committee.

Editor: Liane G. Benning

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References

Abstract | Letter | Acknowledgements | References | Supplementary Information


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Figure 1 [...] Modelled CH4 production, Fe-AOM and SO4-AOM rates are shown in panel d (Dijkstra et al., 2018).
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Our understanding of how anaerobic methanotrophs respond to varying environmental conditions (Holler et al., 2009, 2011; Yoshinaga et al., 2014) and how they might contribute to “cryptic cycles” (the rapid production and consumption of reactive intermediates) in the marine subsurface is constantly evolving (Egger et al., 2018).
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View in article


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AOM metabolisms have been shown to be active from -1 °C to 70 °C (Niemann et al., 2006; Holler et al., 2011), a range of temperatures that is unique and distinguishable from equilibrated thermogenic methane forming in the 100 °C to 250 °C gas window.
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Evidence suggests that these processes can be decoupled (Milucka et al., 2012; Scheller et al., 2016) and metal oxides may also act as terminal electron acceptors (Beal et al., 2009; Cai et al., 2018)
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Anaerobic methanotrophs use enzymes homologous to those used by methanogens (Krüger et al., 2003; Shima et al., 2012), prompting questions regarding the directionality of these metabolisms (Lloyd et al., 2011; Beulig et al., 2019).
View in article


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Work on determining the biochemical pathways of Fe(III) reducing ANME has so far required genetically modifying a methanogen, M. acetivorans with the Mcr from an ANME-1 group organism because unmodified M. acetivorans are unable to be cultured on methane without the modified Mcr (Soo et al., 2016; Yan et al., 2018).
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For instance, axenic cultures of methanogens produce methane with depletions in clumped isotopes relative to the random distribution that reflect kinetic processes (Stolper et al., 2015; Wang et al., 2015; Douglas et al., 2016; Young et al., 2017; Gruen et al., 2018).
View in article
Previous work using one rare isotopologue (Δ13CH3D) suggests that the rate of methanogenesis controls the degree of molecular isotopic equilibrium (Stolper et al., 2015; Wang et al., 2015).
View in article
However, the inability to produce equilibrated methane from axenic cultures has led to speculation that AOM may be responsible for equilibrated environmental methane (Stolper et al., 2015; Wang et al., 2016; Young et al., 2017; Gruen et al., 2018).
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At high concentrations of SO42-, the back reaction produces 3-7 % of the CH4 consumed by AOM, and at low concentrations of SO42- (below 0.5 mM), back reaction can produce as much as 78 % of the CH4 consumed by AOM (Yoshinaga et al., 2014; Timmers et al., 2017).
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Although some of the first steps of methanogenesis may be reversible (Valentine et al., 2004), the final transfer of the methyl group to coenzyme M and the subsequent final hydrogen addition are believed to be irreversible (Gärtner et al., 1994; Thauer, 2011).
View in article


Wang, D.T., Gruen, D.S., Lollar, B.S., Hinrichs, K.-U., Stewart, L.C., Holden, J.F., Hristov, A.N., Pohlman, J.W., Morrill, P.L., Könneke, M. (2015) Nonequilibrium clumped isotope signals in microbial methane. Science 348, 428-431.
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For instance, axenic cultures of methanogens produce methane with depletions in clumped isotopes relative to the random distribution that reflect kinetic processes (Stolper et al., 2015; Wang et al., 2015; Douglas et al., 2016; Young et al., 2017; Gruen et al., 2018).
View in article
In some cases, the clumped isotope composition of environmental microbial methane is consistent with the axenic cultures, but in others it displays a clumped isotope composition reflective of equilibration within the environment of formation (Wang et al., 2015; Young et al., 2017).
View in article
Previous work using one rare isotopologue (Δ13CH3D) suggests that the rate of methanogenesis controls the degree of molecular isotopic equilibrium (Stolper et al., 2015; Wang et al., 2015).
View in article


Wang, D.T., Welander, P.V., Ono, S. (2016) Fractionation of the methane isotopologues 13 CH 4, 12 CH 3 D, and 13 CH 3 D during aerobic oxidation of methane by Methylococcus capsulatus (Bath). Geochimica et Cosmochimica Acta 192, 186-202.
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However, the inability to produce equilibrated methane from axenic cultures has led to speculation that AOM may be responsible for equilibrated environmental methane (Stolper et al., 2015; Wang et al., 2016; Young et al., 2017; Gruen et al., 2018).
View in article


Whiticar, M.J. (1999) Carbon and hydrogen isotope systematics of bacterial formation and oxidation of methane. Chemical Geology 161, 291-314.
Show in context

These challenges are due in part to how methane produced by methanogens inherits characteristics from its substrates (both a range of organic and inorganic carbon) (Conrad, 2005), and they are further complicated when methane is itself the substrate during anaerobic methane oxidation (AOM) (Whiticar, 1999).
View in article


Yan, Z., Joshi, P., Gorski, C.A., Ferry, J.G. (2018) A biochemical framework for anaerobic oxidation of methane driven by Fe (III)-dependent respiration. Nature Communications 9.
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Work on determining the biochemical pathways of Fe(III) reducing ANME has so far required genetically modifying a methanogen, M. acetivorans with the Mcr from an ANME-1 group organism because unmodified M. acetivorans are unable to be cultured on methane without the modified Mcr (Soo et al., 2016; Yan et al., 2018).
View in article


Yoshinaga, M.Y., Holler, T., Goldhammer, T., Wegener, G., Pohlman, J.W., Brunner, B., Kuypers, M.M.M., Hinrichs, K.U., Elvert, M. (2014) Carbon isotope equilibration during sulphate-limited anaerobic oxidation of methane. Nature Geoscience 7, 190-194.
Show in context

Our understanding of how anaerobic methanotrophs respond to varying environmental conditions (Holler et al., 2009, 2011; Yoshinaga et al., 2014) and how they might contribute to “cryptic cycles” (the rapid production and consumption of reactive intermediates) in the marine subsurface is constantly evolving (Egger et al., 2018).
View in article
This back reaction is sensitive to concentrations of the terminal electron acceptor SO42- (Holler et al., 2011; Yoshinaga et al., 2014).
View in article
At high concentrations of SO42-, the back reaction produces 3-7 % of the CH4 consumed by AOM, and at low concentrations of SO42- (below 0.5 mM), back reaction can produce as much as 78 % of the CH4 consumed by AOM (Yoshinaga et al., 2014; Timmers et al., 2017).
View in article


Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.
Show in context

For instance, axenic cultures of methanogens produce methane with depletions in clumped isotopes relative to the random distribution that reflect kinetic processes (Stolper et al., 2015; Wang et al., 2015; Douglas et al., 2016; Young et al., 2017; Gruen et al., 2018).
View in article
In some cases, the clumped isotope composition of environmental microbial methane is consistent with the axenic cultures, but in others it displays a clumped isotope composition reflective of equilibration within the environment of formation (Wang et al., 2015; Young et al., 2017).
View in article
However, the inability to produce equilibrated methane from axenic cultures has led to speculation that AOM may be responsible for equilibrated environmental methane (Stolper et al., 2015; Wang et al., 2016; Young et al., 2017; Gruen et al., 2018).
View in article
This suggests that as energy-rich fractures open, Mcr exposure during the initial step of AOM catalytically exchanges isotopes leaving behind a reservoir that moves closer to thermodynamic equilibrium (Young et al., 2017).
View in article
Figure 3 [...] Bornholm Basin data (magenta diamonds) span between the methanogenesis and AOM zones, while data from Kidd Creek Mine (black to white symbols) (Young et al., 2017) span from the abiotic to AOM zone.
View in article



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Supplementary Information

Abstract | Letter | Acknowledgements | References | Supplementary Information

The Supplementary Information includes:
  • Materials and Methods
  • Tables S-1 to S-3
  • Figures S-1 to S-3
  • Supplementary Information References

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Figures and Tables


Figure 1 Geochemical profiles (±2 σ) from Bornholm Basin from 3-35 MCD. Horizontal grey bar denotes sediments deposited during lacustrine conditions overlain with sediments deposited during brackish marine conditions. Samples were not recovered above the shallow SMTZ. Pink dashed lines denote a shallow (3.3 MCD) and deep (19.8 MCD) SMTZ; only the shallow SMTZ is shown in the bottom panel for clarity. Dark grey vertical bars in e and f denote equilibrium isotopologue compositions for the subsurface temperature of 7.8 ± 0.6 °C. Modelled CH4 production, Fe-AOM and SO4-AOM rates are shown in panel d (Dijkstra et al., 2018

Dijkstra, N., Hagens, M., Egger, M., Slomp, C.P. (2018) Post-depositional vivianite formation alters sediment phosphorus records. Biogeosciences 15, 861-883.

). CH4 production (purple) and SO4-AOM (gold) rates correspond with the upper x axis and Fe-AOM rates (brown) correspond with the lower x axis. SO4-AOM rates above the upper SMTZ are calculated using bottom water SO4 concentrations of 15.0 mM. Additional porewater data shown in Supplementary Information.
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Figure 2 ξ12CH2D2 values (±2 σ) are the most negative at shallow MCD, indicating the greatest departure from equilibrium and approach zero (violet dashed line) with increasing MCD, indicating an approach towards intra-species thermodynamic equilibrium. ΔG values for SO4-AOM and Fe-AOM suggest either metabolism is capable of reversibility (see Supplementary Information).
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Figure 3 Δ12CH2D2 is plotted versus Δ13CH3D. The solid black line represents theoretical thermodynamic equilibrium abundances (with dots representing 100 °C increments from 0-1000 °C). Methane produced by thermogenesis, high temperature abiotic reactions, microbial methanogenesis and low temperature abiotic reactions inhabit unique zones in double isotopologue space. AOM, equilibrating through exchange catalysis during enzymatic back reaction, also inhibits a unique zone: low temperature intra-species thermodynamic equilibrium. Bornholm Basin data (magenta diamonds) span between the methanogenesis and AOM zones, while data from Kidd Creek Mine (black to white symbols) (Young et al., 2017

Young, E., Kohl, I., Lollar, B.S., Etiope, G., Rumble, D., Li, S., Haghnegahdar, M., Schauble, E., McCain, K., Foustoukos, D. (2017) The relative abundances of resolved 12CH2D2 and 13CH3D and mechanisms controlling isotopic bond ordering in abiotic and biotic methane gases. Geochimica et Cosmochimica Acta 203, 235-264.

) span from the abiotic to AOM zone. See Supplementary Information for additional sample description.
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