Abstract
Consumption of methane by aerobic and anaerobic microbes governs the atmospheric level of this powerful greenhouse gas. Whereas a biochemical understanding of aerobic methanotrophy is well developed, a mechanistic understanding of anaerobic methanotrophy has been prevented by the unavailability of pure cultures. Here we report a biochemical investigation of Methanosarcina acetivorans, a methane-producing species capable of anaerobic methanotrophic growth dependent on reduction of Fe(III). Our findings support a pathway anchored by Fe(III)-dependent mechanisms for energy conservation driving endergonic reactions that are key to methanotrophic growth. The pathway is remarkably similar to pathways hypothesized for uncultured anaerobic methanotrophic archaea. The results contribute to an improved understanding of the methane cycle that is paramount to understanding human interventions influencing Earth’s climate. Finally, the pathway enables advanced development and optimization of biotechnologies converting methane to value-added products through metabolic engineering of M. acetivorans.
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Discover the latest articles, news and stories from top researchers in related subjects.Introduction
The production and consumption of methane is a component of the global carbon cycle. An end product of the anaerobic decomposition of biomass, nearly one billion tons of methane is produced each year in diverse anaerobic habitats of the Earth’s terrestrial biosphere1. Methane is also produced in anaerobic marine sediments and released from vast reservoirs of gas hydrates (5.0 × 105–1.0 × 107 Tg)2. Methane is an important greenhouse gas nearly 20-fold more potent than CO23. Fortunately, release to the atmosphere is mitigated by the aerobic and anaerobic oxidation of methane or assimilation into cell biomass by microbes that ultimately control the Earth’s climate4.
The anaerobic oxidation of methane (AOM) requires reduction of electron acceptors (Fe(III), Mn(IV), nitrate or sulfate) to be thermodynamically favorable5,6. Until recently, it was thought that AOM in marine sediments required a symbiosis of anaerobic methanotrophic archaea (ANME) and sulfate-reducing species for which the latter utilizes reductant produced by the former to make the overall reaction thermodynamically favorable. However, the artificial electron acceptor AQDS (9,10-anthraquinone-2,6-disulfonate), a surrogate for humic substances in the environment, decouples methane oxidation from sulfate reduction in marine sediments presenting the possibility of independent respiratory AOM and growth of usually syntrophic ANME-27,8. Indeed, respiratory AOM is in accordance with the occurrence of solitary ANME in microbial mats and sediments from diverse anaerobic environments9. Furthermore, incubations of environmental samples with Fe(III)-citrate yielded biosynthetic activity exclusive to uncultured ANME-2c and other ANME-2 cells7. These results inspired the hypotheses that symbiotic associations of ANME and sulfate-reducing species evolved from methanogenic species that first acquired the ability to conserve energy by oxidizing methane and reducing metal oxides7. Fe(III)-dependent AOM reported for a culture enriched in ‘Candidatus Methanoperedens nitroreducens’ presents the possibility of Fe(III)-dependent respiratory growth although not yet documented10. AOM dependent on reduction of Fe(III) is of particular biogeochemical interest. Indeed, it is proposed that if only a small percentage of current global Mn(IV) and Fe(III) influx is used for AOM, it has the potential to consume a large amount of methane11. It is also proposed that Fe(III)-dependent AOM was largely responsible for oxidizing the entirety of methane produced on early Earth prior to the advent of oxygen11.
The prospect that ANME are capable of independent AOM and growth by Fe(III) respiration profoundly changes current views of AOM and iron cycling in Nature, prompting further investigation. It is conjectured that ANME grow by reverse methanogenesis based on environmental metagenomic and metatranscriptomic analyses of sediments5,6. However, reversal and growth requires mechanisms for energy conservation and overcoming endergonic reactions yet to be investigated biochemically5,6. Clearly, biochemical approaches with pure cultures are necessary to obtain a rigorous understanding of AOM. Although discovered nearly four decades ago, the unavailability of pure cultures has prevented biochemical investigations of AOM. However, a culture enriched in ‘Candidatus Methanoperedens nitroreducens’ is capable of AOM dependent on reduction of nitrate-, nitrite- or Fe(III)10,12. Furthermore, Methanosarcina acetivorans strain C2A is capable of trace methane oxidation (TMO) defined as reverse methanogenesis during net methane production from growth substrates in the absence of external electron acceptors6,13,14. TMO contrasts with AOM which is independent of methanogenesis and requires electron acceptors with or without a syntrophic partner. More recently, Fe(III)-dependent AOM was documented for a strain of M. acetivorans engineered to produce methyl-coenzyme M methyl reductase (Mcr) derived from ANME-1 sediments15. Thus, M. acetivorans has emerged as a model for advancing a biochemical understanding of AOM. M. acetivorans is also recognized as instrumental in development of biomanufacturing processes converting methane into value-added products16,17,18. Here we report a biochemical investigation of wild-type M. acetivorans that supports an AOM pathway anchored by Fe(III)-dependent respiration generating ion gradients that supply the energy to drive endergonic reactions essential for AOM and growth. The results provide a deeper mechanistic understanding of AOM and iron cycling in Nature, and a guide for optimization of methane-based biotechnologies.
Results
Biochemistry of M. acetivorans resembles proposals for AOM
Mechanisms for energy conservation and driving endergonic reactions are key to reversing methanogenesis and methanotrophic growth (AOM). Based on environmental metagenomic and transcriptomic analyses, AOM pathways are proposed for ANME that include membrane-bound components involved in energy conservation (Rnf and Fpo complexes), electron transport (CoMS-SCoB heterodisulfide reductase (HdrDE); multi-heme c-type cytochromes (MHC); and methanophenazine (MP)) and methyl transfer (methyl-tetrahydrosarcinapterin:coenzyme M methyltransferase (Mtr))5,6,19,20,21. These components are essential to biochemically characterized methanogenic pathways in M. acetivorans strain C2A. Thus, the components were investigated in strain C2A to provide a biochemical understanding of roles in AOM of ANME.
Driving endergonic methane oxidation to the methyl level
The finding that both acetate and CO2 are produced during TMO and AOM by M. acetivorans indicates a dependence on reversal of acetoclastic and CO2-reducing methanogenic pathways, albeit with essential modifications13,14,15. The first two reactions required for reversal are methane oxidation yielding methyl-coenzyme M (CH3-SCoM) and transfer of the methyl group to tetrahydrosarcinapterin (H4SPT). Both reactions are endergonic (Supplementary Table 1). The coenzyme M (HSCoM) and coenzyme B (HSCoB) products are oxidized to the heterodisulfide (CoMS-SCoB) which is the electron acceptor for the methane oxidation reaction yielding CH3-SCoM and HSCoB. The exergonic oxidation of HSCoM and HSCoB coupled to Fe(III) reduction is a potential mechanism driving the endergonic methane oxidation and methyl transfer reactions (Supplementary Table 1). This was tested by monitoring HSCoM and HSCoB oxidation by everted membrane vesicles prepared from acetate-grown M. acetivorans. The initial rate of free thiol consumption by vesicles loaded with S-layer-permeable Fe(III) citrate and AQDS (46.2 nmol/min/mg vesicle protein) is 2.5- and 12.1-fold greater than the rate by vesicles loaded with only AQDS (18.5 nmol/min/mg vesicle protein) or only Fe(III) citrate (3.8 nmol/min/mg vesicle protein) (Fig. 1). As HdrDE is the only membrane-bound heterodisulfide reductase22,23,24, the results show that HdrDE oxidizes HSCoM/HSCoB with transfer of electrons to Fe(III) mediated by AQDS with the potential for product removal driving the endergonic oxidation of methane and transfer of the methyl group to H4SPT.
Generation of a sodium gradient
Two membrane-bound complexes generate a Na+ gradient (high outside) in the acetoclastic pathway of M. acetivorans22. The Rnf complex catalyzes the vectorial translocation of Na+ generating a gradient (high outside) when oxidizing ferredoxin (FdxR) with transfer of electrons to an electron transport chain culminating in reduction of CoMS-SCoB25,26,27. A Na+ gradient is also generated by the exergonic transfer of the methyl group from CH3-H4SPT to HSCoM by the methyltransferase (Mtr)22. A Rnf homolog plays a role in generating a Na+ gradient in the AOM pathway proposed for an uncultured ANME-2a organism based on the metagenome and transcriptome6,19,21. This known biochemistry raised the question of whether oxidation of FdxR by everted vesicles of M. acetivorans is coupled to reduction of Fe(III) that drives formation of a Na+ gradient of sufficient magnitude to reverse the exergonic methyl transfer catalyzed by Mtr necessary for reversal of the acetoclastic and CO2-reduction methanogenic pathways.
Fe(III)-loaded everted vesicles catalyze FdxR:Fe(III) oxidoreductase (ORase) activity independent of AQDS and with rates similar to that of vesicles loaded with both AQDS and Fe(III), although sixfold greater than that of vesicles loaded with only AQDS (Supplementary Fig. 1). The rate of Fe(III)-dependent FdxR oxidation is fourfold less with vesicles prepared from methanol-grown cells, a result consistent with a role for the Rnf complex that is downregulated in methanol- vs. acetate-grown M. acetivorans25,26,28. Furthermore, Rnf is the only membrane-bound system capable of oxidizing FdxR23,25,27. The results establish that oxidation of FdxR is coupled to the reduction of Fe(III) (ΔEo´ = 1.17 V) capable of generating a Na+ gradient driving reversal of methyl transfer by Mtr.
A multi-heme c-type cytochrome (MHC), abundant in membranes of acetate-grown M. acetivorans, is reduced with FdxR and re-oxidized by addition of Fe(III)-citrate independent of AQDS (Supplementary Fig. 2), indicating a role for MHC in FdxR:Fe(III) ORase activity26. The failure of AQDS to enhance FdxR:Fe(III) ORase activity in everted vesicles (Supplementary Fig. 1) indicates direct transfer of electrons from a membrane-bound electron carrier to soluble Fe(III) citrate. The MHC is a strong candidate as it is the direct electron acceptor of the Rnf complex that oxidizes FdxR25,27. Whole cells reduce insoluble ferrihydrite with CO as the electron donor for which the initial rate is stimulated fourfold in the presence of AQDS, albeit fourfold less than with Fe(III) citrate (Supplementary Fig. 3). This result indicates that AQDS is essential to mediate electron transfer to insoluble Fe(III) oxides.
The FdxR:Fe(III) ORase activity of Fe(III) citrate-loaded everted vesicles is stimulated fourfold by the addition of NaCl to the reaction mixture that is concentration dependent with a Km of ~1.0 mM (Supplementary Fig. 1). The stimulation is confirmed with vesicles loaded with both AQDS and Fe(III) citrate. The results are consistent with Na+ translocation into the lumen driven by electron transport. The apparent translocation of Na+ was further investigated with 22Na+ that rapidly accumulates in everted vesicles (25 nmol/mg protein/min) dependent on Fe(III) and FdxR (Fig. 2a). The Na+ ionophore ETH157 abolishes accumulation. These results establish that membranes translocate Na+ coupled to electron transport from FdxR to Fe(III). The protonophore CCCP (carbonyl cyanide m-chlorophenyl hydrazine) has no effect on the rate of Na+ accumulation which precludes that Na+ translocation is a secondary effect driven by a primary H+ gradient combined with a Na+/H+ antiporter. Accumulation of Fe(II) in vesicles correlates with accumulation of 22Na+ for each experimental condition except as expected for addition of ETH157 (Fig. 2b). Vesicles loaded with Fe(III) completely oxidize limiting amounts of fully reduced FdxR2- (2.5 nmol) and accumulate a total of 4.7 ± 0.4 (n = 3) nmol Fe(II) consistent with the expected stoichiometry. The ratio of 22Na+/Fe(II) is 1.8 ± 0.2 indicating translocation of two Na+/electron transported. Generation of a Na+ gradient by Rnf and the highly exergonic Fe(III)-dependent oxidation of the reaction product HSCoM by HdrDE are potential mechanisms for driving the endergonic methyl transfer reaction by Mtr.
Driving endergonic methyl transfer
It was next asked if the Na+ gradient generated by FdxR:Fe(III) ORase activity is of sufficient magnitude to drive the endergonic methyl transfer from CH3-SCoM to H4SPT by Mtr. Tetrahydrofolate (THF), a functional homolog of H4SPT, was used in the experiments29. Membranes catalyze methyl transfer in the thermodynamically favorable direction of CH3-SCoM synthesis with the methyl group donated by CH3-THF (Supplementary Fig. 4). The maximum initial rate of activity (180.8 ± 4.2 nmol/min/mg protein) is dependent on carbon monoxide (CO) and adenosine triphosphate (ATP), a result characteristic of reductive activation for Mtr of Methanosarcina species29. Everted membrane vesicles catalyze Fdx- and Fe(III)-dependent methyl transfer from CH3-SCoM to THF with an initial rate of 9.8 ± 1.2 nmol/min/mg protein that is abolished by the Na+ ionophore ETH157 (Fig. 3). The presence of ATP stimulates the initial rate to 26.5 ± 0.9 nmol/min/mg protein consistent with results reported for Mtr29. The results demonstrate that the Na+ gradient generated by FdxR:Fe(III) ORase activity is of sufficient magnitude to drive the endergonic methyl transfer from CH3-SCoM to H4SPT.
Conservation of energy
The mechanisms by which energy is conserved in ATP for growth of ANME is of fundamental importance in addition to mechanisms driving essential endergonic reactions. Substrate-level phosphorylation catalyzed by acetate kinase is a potential mechanism for ATP synthesis when considering acetate is a product of AOM by M. acetivorans15. Another possibility is ATP synthesis catalyzed by the ATP synthase which is dependent on both Na+ and H+ gradients30. This mechanism requires generation of a H+ gradient to accompany the Na+ gradient generated by FdxR:Fe (III) ORase activity. The membrane-bound Fpo complex catalyzes a vectorial translocation of H+ generating a gradient (high outside) by oxidizing coenzyme F420H2 with transfer of electrons to HdrDE (F420H2:CoB-S-SCoM ORase activity)31. Based on metagenomic and transcriptomic analyses, Fpo homologs are proposed to play a role in generating H+ gradients in AOM pathways based on metagenomic and metatranscriptomic analyses of ANME5,19,20,21,32 which prompted asking if the oxidation of F420H2 by the Fpo of M. acetivorans is coupled to reduction of Fe(III) (F420H2:Fe(III) ORase activity) that also generates a H+ gradient. Fpo activity is substantial in methanol-grown M. acetivorans28,33 from which Fe(III) citrate-loaded everted membrane vesicles were prepared to evaluate F420H2:Fe(III) ORase activity. The vesicles catalyze Fe(III)-dependent F420H2 oxidation (Supplementary Fig. 5) with a sevenfold stimulation of the initial rate upon addition of the protonophore CCCP, indicating electron transport coupled to H+ translocation. The rate is fourfold less with vesicles from acetate-grown cells corresponding to fivefold less Fpo, a result supporting a role for Fpo in Fe(III)-dependent F420H2 oxidation. Vesicles accumulate a total of 11.2 ± 1.1 nmol (n = 3) Fe(II) in reaction mixtures containing 5.0 nmol F420H2 that is oxidized to completion (not shown), a result expected for the obligate two-electron carrier34. Negligible Fe(II) is produced in the absence of F420H2 or Fe(III).
The finding that CCCP stimulates F420H2-dependent reduction of Fe(III) prompted experiments to determine if the highly exergonic electron transport (ΔEo´ = 1.15 V) is coupled to vectorial pumping of H+ from the medium into the lumen of everted vesicles loaded with Fe(III) citrate (Fig. 4). Addition of F420H2 produces rapid alkalinization of the medium followed by gradual acidification towards stabilization of the pH (Fig. 4a). The ATPase inhibitor, N,N’-dicyclohexylcarbodiimide (DCCD), has no effect on H+ translocation, ruling out a role for ATP-driven translocation. Negligible alkalinization and re-acidification is observed with vesicles devoid of Fe(III) or when F420 replaces F420H2 (not shown). Increased concentrations of the protonophore CCCP (carbonyl cyanide m-chlorophenyl hydrazine) correlate with decreased F420H2-dependent alkalinization (Fig. 4b). The results demonstrate that the electron transport is coupled to translocation of H+ from the medium into the lumen. Increased alkalinization correlates with increased amounts of F420H2 from which it is calculated that 2.1 H+ enters into the lumen per F420H2 oxidized (Fig. 4c). However, the results indicate translocation of 4 H+ when considering 2 H+ are produced outside the vesicle upon oxidation of F420H2. The result is consistent with the stoichiometry predicted for the F420H2:CoMS-SCoB ORase activity of Methanosarcina species35. Although all the electron transfer components have yet to be determined, the results establish that F420H2:Fe(III) ORase activity is coupled to generation of a H+ gradient with the potential to assist in ATP synthesis by the Na+- and H+-dependent ATP synthase.
Proposed pathway of Fe(III)-dependent AOM and methanotrophic growth
Acetate and CO2 are products of Fe(III)-dependent AOM by M. acetivorans indicating reversal of both acetoclastic and CO2-reducing methanogenic pathways15. Figure 5 shows a pathway proposed for soluble Fe(III)-dependent AOM by M. acetivorans based on results presented here and characterized components of the well-established acetoclastic and CO2-reducing methanogenic pathways of M. acetivorans23,25,26,27,28,33,36,37. As the outer S-layer of M. acetivorans contains pores of sufficient size to permit passage of Fe(III)-citrate, results obtained with everted vesicles can be extrapolated to whole cells38.
In the proposed pathway (Fig. 5), methane is assumed oxidized by the methyl-coenzyme M methyl reductase (Mcr) (Rxn. 1) based on TMO and AOM by M. acetivorans that requires Mcr activity13,14,15. The methyl group of CH3-SCoM is then transferred to H4SPT by the membrane-bound methyltransferase (Mtr) (Rxn. 2). The results presented show the endergonic reaction is driven by the Na+ gradient generated with FdxR:Fe(III) ORase activity catalyzed by the Rnf complex (Rxn. 3)23,27. The results also indicate that MHC is the direct electron donor to Fe(III), analogous to reduction of soluble and insoluble forms of Fe(III) by the MHC of Fe(III) reducing microbes such as Shewanella oneidensis39,40.
The HSCoM and HSCoB products of reactions 1 and 2 are oxidized to regenerate CoMS-SCoB essential for Mcr-catalyzed methane oxidation (Rxn. 1). The results presented indicate the oxidation is catalyzed by the membrane-bound HdrDE (Rxn. 4) dependent on AQDS-mediated reduction of Fe(III). The endergonic oxidation of methane (Rxn. 1) is driven by exergonic reaction 4 coupled with reaction 2 driven by exergonic reaction 3 (Supplementary Table 1). The path of AQDS-dependent electron transport from HdrDE to Fe(III) is unknown. MP is a quinone-like, membrane-intrinsic, electron carrier that donates to cytochrome b in all pathways of methanogenesis by M. acetivorans23,27. Although reduction of MP by cytochrome b is expected, MPH2 is also expected to directly reduce Fe(III) analogous to abiotic reduction of AQDS41,42 obviating a requirement for AQDS in contrast to that observed. Thus, a more plausible pathway involves a role for AQDS accepting electrons from cytochrome b of the membrane-intrinsic HdrE and AQDS abiotically reducing Fe(III) (Fig. 5).
It is proposed that the methyl group of CH3-H4SPT enters branched pathways for production of acetate (Rxns. 5–6) and oxidation to CO2 (Rxns. 7–8). Transfer of electrons to Fe(III) in the CO2 oxidation branch is essential for the overall pathway to be thermodynamically favorable (Supplementary Table 1). The acetate branch is included based on previous findings that acetate is a product of Fe(III)-dependent AOM by M. acetivorans15. The exergonic reactions leading to acetate are experimentally validated for the pathway of CO-dependent growth by M. acetivorans33. Reactions proposed for oxidation of the methyl group of CH3-H4SPT to CO2 (Rxns. 7 and 8) are components of the CO2-reduction pathway of M. acetivorans33. The pathway (Fig. 5) proposes that the F420H2 produced is re-oxidized with transfer of electrons to Fe(III) by two possible mechanisms. The first is by exergonic F420H2:Fe(III) ORase activity coupled to the generation of a H+ gradient (Rxn. 9) involving Fpo that is also essential to the CO2-reduction pathway of M. acetivorans33. Although the path of electron transfer from F420H2 to Fe(III) is unknown, failure of AQDS to stimulate F420H2:Fe(III) ORase activity indicates electron transfer from Fpo to Fe(III) is independent of AQDS and HdrDE in contrast to electron transport from HdrDE to Fe(III). A role for MP is possible as it is the electron acceptor for Fpo23,35. It is proposed that the MPH2 generated is oxidized by Fe(III) contributing to the H+ gradient (Fig. 5, Rxn. 9). Alternatively, F420H2 may be oxidized by the recently characterized electron bifurcating HdrA2B2C2 of M. acetivorans (Rxn. 10) with transfer of electrons to FdxO (Rxn. 11) and CoMS-SCoB (Rxn. 12)43. Oxidation of HSCoM and HSCoB (Rxn. 13) is postulated to be accomplished by HdrDE with exergonic transfer of electrons to Fe(III) dependent on AQDS analogous to reaction 4.
Finally, it is proposed that the ratio of acetate/CO2 produced is flexible and governs the ratio of Na+/H+ gradients requiring the multi-subunit Na+/H+ antiporter Mrp (Rxn. 14) to adjust the Na+/H+ ratio optimal for the ATP synthase shown previously to be dependent on both Na+ and H+ (Rxn. 15)30,44.
Discussion
The proposed biochemical-based pathway elevates AOM by M. acetivorans to a fundamental mechanistic level of understanding. The pathway is essentially a reversal of the biochemically characterized acetoclastic and CO2-reduction methanogenic pathways, albeit dependent on reduction of Fe(III). The results reveal the role Fe(III) plays in energy conservation and driving endergonic reactions that support methanotrophic growth15. Abundant methane is targeted for development of recently advocated biomanufacturing processes converting it to liquid biofuels and value-added products16. Thus, the pathway provides a guide for optimization of existing, and development of advanced, biotechnologies facilitated by the timely announcement of a cas9-mediated genome editing system for facile metabolic engineering of M. acetivorans16,17,18,45,46,47.
The proposed M. acetivorans pathway is remarkably similar to the pathway proposed for ANME-2a based on the single-aggregate genome derived from integrated environmental metagenomic and transcriptomic analyses of a marine environment21. The M. acetivorans and ANME-2a pathways both include Rnf, Fpo, MHC, HdrDE and CO dehydrogenase/acetyl-CoA synthase for which the homologs show robust amino acid sequence identities (Supplementary Table 2). The results presented, showing generation of Na+ and H+ ion gradients by Rnf and Fpo of M. acetivorans, validate the same roles for Rnf and Fpo in pathways proposed for uncultured ANME20,21,32. The pathways for M. acetivorans, ANME-1, ANME-2a and ANME-2d include acetate as a product12,21,32. Furthermore, analysis of methane seep sediments show robust 13C depletion in acetate with δ13C values near −90%48. These results suggest that the proposed AOM pathway of M. acetivorans is largely representative of ANME, further strengthened by data showing ANME-1, ANME-2d and ANME-2a are phylogenetically related to Methanosarcina species10,20,21,49. The one exception is Mcr of wild-type M. acetivorans which could explain why only the engineered strain containing Mcr from ANME-1 is capable of Fe(III)-dependent AOM15. No other genetic alterations were imposed on the engineered strain ensuring that mechanisms for Fe(III)-dependent energy conservation and driving endothermic reactions are identical to those investigated in the wild type. Although TMO by wild-type M. acetivorans indicates that Mcr catalyzes the reverse reaction analogous to that of Methanothermobacter marburgensis50, bias in the direction of methane formation may be a kinetic block to initiating AOM as opposed to a more favorable rate of methane oxidation for Mcr of ANME.
The similarity in pathways for M. acetivorans and proposed for ANME-2a strengthen the prospect of Fe(III)-dependent AOM and respiratory growth by uncultured ANME. Importantly, the roles shown for Rnf, MHC, Fpo and HdrDE in electron transfer to Fe(III) by M. acetivorans are also hypothesized for ANME-2 in transfer of electrons to metal oxides or the syntrophic partner19. The MHCs of ANME-2 are proposed to extend beyond the S-layer to facilitate the electron transfer. The results presented here indicate that soluble Fe(III) citrate is reduced by the MHC of M. acetivorans. It is conceivable that the MHC also plays a role in reducing insoluble forms of Fe(III). If so, either multiple MHCs extend to the outer S-layer of M. acetivorans or diffusible electron carriers such as low-molecular-mass humic acids or secreted flavins mediate electron transfer between the MHC and the S-layer7,51. The latter is consistent with the finding that AQDS, a surrogate for humics, stimulated ferrihydrite reduction in whole cells of M. acetivorans. Extension of MHCs to the outer S-layer is consistent with MHCs from ANME-2a and ANME-2d reported to be fused with a putative S-layer domain homologous to the S-layer protein of M. acetivorans19.
The pathway proposed for M. acetivorans is also consistent with the hypothesis that symbiotic associations of ANME and sulfate-reducing species evolved from methanogenic species that first acquired the ability to conserve energy by oxidizing methane coupled to reduction of metal oxides7. However, it is also possible that the ancestor common to M. acetivorans and ANME first performed AOM with a sulfate reducer and then switched to reduction of metal oxides. Unlike methanogenesis pathways, the proposed AOM pathway of M. acetivorans features multiple roles for heterodisulfide reductases (Fig. 5). Two types of heterodisulfide reductases are essential to all methanogenic pathways, the cytoplasmic HdrABC and the membrane-associated HdrDE23,24. The results presented here support a role for HdrDE coupled to AQDS-mediated reduction of Fe(III) that drives the endergonic methane oxidation and methyl transfer reactions essential to reversal. A role is proposed for the electron bifurcating HdrA2B2C2 in energy conservation when generation of Na+ and H+ gradients by Rnf and Fpo (Fig. 5, Rxns. 3 and 9) are limited by the availability of Fe(III). The HdrA2B2C2 plays this role by diverting electron flow from F420H2 to FdxO promoting acetate production and ATP synthesis by substrate-level phosphorylation (Fig. 5, Rxns. 5 and 6). Notably, the genome of the ANME ‘Candidatus Methanoperedens nitroreducens’ encodes a homolog of HdrA2 that is the flavin-containing electron-bifurcating subunit of HdrA2B2C243,52.
A role for H2 in electron transport and energy conservation is unlikely for Fe(III)-dependent AOM. M. acetivorans is incapable of metabolizing H2 which contrasts with other species of Methanosarcina for which ATP synthesis is dependent on the production and consumption of H2 to generate H+ gradients23. The thermodynamically unfavorable production of H2 as an electron transfer agent could impose a barrier to reversing methanogenesis. Metagenomic analyses of the ANME-2a clade, phylogenetically related to M. acetivorans, are devoid of hydrogenase genes21. Thus, the ANME-2a clade is unlikely to employ H2 for transferring electrons to syntrophic partners. It is more likely that electrons are transferred via DIET (direct interspecies electron transfer) as previously hypothesized for uncultured species of the ANME-2 clade19. Pathways proposed for ANME include acetate as a product, although disputed as a diffusible electron carrier in syntrophic AOM12,19,21,32,53. If not involved in syntrophic AOM, acetate may be an essential carbon source for the syntrophic partner21. A portion of acetyl-CoA in the pathway of acetate production (Fig. 5) may also enter biosynthetic pathways essential for AOM by ANME and M. acetivorans54.
In addition to AOM, M. acetivorans is capable of TMO producing CO2 or acetate during net methane production when grown with methanogenic substrates in the absence of exogenous electron acceptors13,14. Although TMO is likely dependent on reversal of carbon transformation reactions in acetoclastic or CO2-reducing methanogenic pathways (Fig. 5), endergonic reactions of TMO are driven by energy conservation dependent on methanogenesis rather than reduction of Fe(III).
Methods
Cell growth and materials
Methanosarcina acetivorans wild-type strain C2A, isolated from marine sediment, was grown with acetate or methanol as previously described55,56. The CO dehydrogenase/acetyl-CoA synthase (CODH/ACS) was purified from acetate-grown cells as previously described43. The ferredoxin (Fdx) upregulated in acetate-grown M. acetivorans was heterologously produced and purified as previously described43. Purification of F420 from methanol-grown cells and preparation of F420H2 was as described elsewhere57. AQDS was purchased from ACROS Organics and HSCoB from Tocris Bioscience. CoMS-SCoB heterodisulfide was prepared as described elsewhere57. HSCoM, THF and CH3-THF were purchased from Sigma Chemical.
Membrane fragments were isolated as described previously27. Washed everted membrane vesicles were prepared as described elsewhere except 5 mM ferric citrate or 5 mM AQDS were included in buffers prior to French pressure cell lysis to load vesicles with either or both electron acceptor where indicated25,57. The integrity of vesicles was determined by artificial energization as described elsewhere30. Maximum quenching of acridine orange was within 5 s followed by 37% dequenching over a period of 4 min.
Activity assays
All activity assays were performed anaerobically at 21 °C in serum-stoppered glass vials with the indicated gas atmosphere. Pre-reduced Fdx was prepared by incubation with CODH/ACS in 1.0 Atm CO followed by replacement of CO with Ar. The same procedure was used for assays requiring continuous reduction of Fdx except the CO was present throughout the assay. Additions and samplings were performed with gas-tight syringes. Contents of reaction mixtures are included in Figure captions.
The reduced ferredoxin (FdxR):Fe(III) oxidoreductase activity of vesicles was monitored spectrophotometrically following the oxidation of pre-reduced Fdx. Activity was based on the change of absorbance at 410 nm (ε = 30.0 mM−1 cm−1). Measurement of Na+ translocation was as previously described with the following modifications25. The reaction mixture was incubated in 1.0 Atm CO for 40 min to ensure Na+ equilibrium prior to addition of CODH/ACS to start the reaction. At the time points indicated, the external 22Na was removed from samples (100 μl) using a column (0.5 × 3 cm) of DOWEX 50WX8 (Sigma). The vesicles were eluted with 1.0 ml of 0.4 M sucrose followed by addition of 9.0 ml of Ultima Gold LLT scintillation fluid (Perkin Elmer) and measurement of radioactivity with a LSC Beckman Coulter Model LS6500 liquid scintillation counter. The Na+ concentration of the reaction mixture was determined with a Ross Sure-Flow (Thermo Fisher Scientific) Na+-selective combination electrode.
F420H2:Fe(III) oxidoreductase activity of vesicles was monitored spectrophotometrically following oxidation of F420H2. Activity was based on the change of absorbance at 420 nm (ε = 41.4 mM−1 cm−1). Measurement of H+ translocation was as described elsewhere57 with the following modifications. An Inlab MicroTM (Mettler-Toledo) pH electrode was connected to a EPU353 pH/ISE isoPODTM (eDAQ) pH meter interfaced to a computer through Pod-VuTM software (eDAQ) to monitor the pH change with time. Additions of F420H2 were made with a gas-tight syringe through the rubber stopper. The pH changes were calibrated with standard solutions of KOH.
The forward and reverse CH3-THF:HSCoM methyltransferase activities of vesicles were performed as described elsewhere29. Forward activity was monitored by detection of thiol group consumption on transfer of the methyl group from CH3-THF to HSCoM. Reverse activity was monitored by detection of HSCoM production on transfer of the methyl group of CH3-SCoM to THF.
Reverse heterodisulfide reductase activity (HSCoM+HSCoB→CoMS-SCoB+2H+) was assayed as previously described except activity was monitored by consumption of thiol groups58.
Analytical
Production or consumption of HSCoM and HSCoB was determined with Ellman’s reagent59. Determination of Fe(II) was by the ferrozine method described elsewhere60. Vesicles were collected from the reaction mixture by centrifuging at 135,000 × g for 60 min. CHAPS (15 mM) was added to dissolve vesicles and release Fe(II) prior to analysis. Protein was estimated with the Bradford assay kit (Bio-Rad Laboratories) using bovine serum albumin as the protein standard61.
Data availability
All relevant data are available from the authors.
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Acknowledgements
This work was supported by: the Department of Energy Advanced Research Projects Agency-Energy #0881-1525 to J.G.F. (70%); the Division of Chemical Sciences, Geosciences and Biosciences, Office of Basic Energy Sciences of the US Department of Energy through grant DE-FG02-95ER20198 (20%); the Person endowment to J.G.F. (10%); and the US National Science Foundation Division of Earth Sciences (award GEO-1451593) to C.A.G.
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J.G.F. and Z.Y. devised the study. Z.Y. conducted the experiments. P.J. and C.A.G. assisted with the 22Na experiments. J.G.F. and Z.Y. analyzed the data and wrote the manuscript.
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Yan, Z., Joshi, P., Gorski, C.A. et al. A biochemical framework for anaerobic oxidation of methane driven by Fe(III)-dependent respiration. Nat Commun 9, 1642 (2018). https://doi.org/10.1038/s41467-018-04097-9
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DOI: https://doi.org/10.1038/s41467-018-04097-9
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