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Published in final edited form as: Nat Microbiol. 2017 May 30;2:17081. doi: 10.1038/nmicrobiol.2017.81

Discovery of extremely halophilic, methyl-reducing euryarchaea provides insights into the evolutionary origin of methanogenesis

Dimitry Y Sorokin 1,2,*, Kira S Makarova 3, Ben Abbas 2, Manuel Ferrer 4, Peter N Golyshin 5, Erwin A Galinski 6, Sergio Ciordia 7, María Carmen Mena 7, Alexander Y Merkel 1, Yuri I Wolf 3, Mark CM van Loosdrecht 2, Eugene V Koonin 3,*
PMCID: PMC5494993  NIHMSID: NIHMS869520  PMID: 28555626

Abstract

Methanogenic archaea are major players in the global carbon cycle and in the biotechnology of anaerobic digestion. The phylum Euryarchaeota includes diverse groups of methanogens that are interspersed with non-methanogenic lineages. So far methanogens inhabiting hypersaline environments have been identified only within the order Methanosarcinales. We report the discovery of a deep phylogenetic lineage of extremophilic methanogens in hypersaline lakes, and present analysis of two nearly complete genomes from this group. Within the phylum Euryarchaeota, these isolates form a separate, class-level lineage “Methanonatronarchaeia” that is most closely related to the class Halobacteria. Similar to the Halobacteria, “Methanonatronarchaeia” are extremely halophilic and do not accumulate organic osmoprotectants. The high intracellular concentration of potassium implies that “Methanonatronarchaeia” employ the “salt-in” osmoprotection strategy. These methanogens are heterotrophic methyl-reducers that utilize C1-methylated compounds as electron acceptors and formate or hydrogen as electron donors. The genomes contain an incomplete and apparently inactivated set of genes encoding the upper branch of methyl group oxidation to CO2 as well as membrane-bound heterosulfide reductase and cytochromes. These features differentiates “Methanonatronarchaeia” from all known methyl-reducing methanogens. The discovery of extremely halophilic, methyl-reducing methanogens related to haloarchaea provides insights into the origin of methanogenesis and shows that the strategies employed by methanogens to thrive in salt-saturating conditions are not limited to the classical methylotrophic pathway.

Introduction

Methanogenesis is one of the key terminal anaerobic processes of the biogeochemical carbon cycle both in natural ecosystems and in industrial biogas production plants 1,2. Biomethane is a major contributor to global warming 3. Methanogens comprise four classes, “Methanomicrobia”, Methanobacteria, Methanopyri and Methanococci, and part of the class Thermoplasmata, within the archaeal phylum Euryarchaeota47. The recent metagenomic discovery of putative methyl-reducing methanogens in the Candidate phyla “Bathyarchaeota” 8 and “Verstaraetearchaeota” 9 indicates that methanogenesis might not be limited to Euryarchaeota.

Three major pathways of methanogenesis are known1,2: hydrogenotrophic (H2, formate and CO2/bicarbonate as electron acceptor), methylotrophic (dismutation of C1 methylated compounds to methane and CO2) and acetoclastic (dismutation of acetate into methane and CO2). In the hydrogenotrophic pathway, methane is produced by sequential 6-step reduction of CO2. In the methylotrophic pathway, methylated C1 compounds, including methanol, methylamines and methylsulfides, are first activated by specific methyltransferases. Next, one out of four methyl groups is oxidized through the same reactions as in the hydrogenotrophic pathway occurring in reverse, and the remaining three groups are reduced to methane. In the acetoclastic pathway, methane is produced from the methyl group after activation of acetate. The only enzyme that is uniquely present in all three types of methanogens is methyl-CoM reductase, a Ni-corrinoid protein catalyzing the last step of methyl group reduction to methane 1012.

The recent discovery of methanogens among Thermoplasmata 5,1315 drew attention to the fourth, methyl-reducing, pathway, previously characterized in Methanosphaera stadtmanae (Methanobacteria) and Methanomicrococcus blatticola (“Methanomicrobia”) 1620. In this pathway, C1 methylated compounds are used only as electron acceptors, whereas H2 serves as electron donor. In the few known representatives, the genes for methyl group oxidation to CO2 are either present but inactive (Methanosphaera) 16 or completely lost (Thermoplasmata methanogens) 67. Recent metagenomic studies have uncovered three additional, deep lineages of potential methyl-reducing methanogens, namely, Candidate class “Methanofastidiosa” within Euryarchaeota 21 and Candidate phyla “Bathyarchaeota” and “Verstraetearchaeota” 8,9, supporting the earlier hypothesis that this is an independently evolved, ancient pathway 22.

The classical methylotrophic pathway of methanogenesis that has been characterized in moderately halophilic members of Methanosarcinales 23, apparently dominates in hypersaline conditions 2325. In contrast to the extremely halophilic haloarchaea, these microbes only tolerate saturated salt conditions but optimally grow at moderate salinity (below 2–3 M Na+) using organic compounds for osmotic balance (“salt-out” strategy) 26,27.

Our recent study of methanogenesis in hypersaline soda lakes identified methylotrophic methanogenesis as the most active pathway. In addition, culture-independent analysis of the mcrA gene, a unique marker of methanogens, identified a deep lineage that is only distantly related to other methanogens 28. We observed no growth of these organisms upon addition of substrates for the classical methanogenic pathways and concluded that they required distinct growth conditions. Here we identify such conditions and describe the discovery and physiological, genomic and phylogenetic features of a previously overlooked group of extremely halophilic, methyl-reducing methanogens.

Discovery of an unknown deep lineage of extremely halophilic methanogens in hypersaline lakes

Sediment stimulation experiments

Two deep-branching mcrA sequences have been previously detected in sediments from hypersaline soda lakes in south-eastern Siberia 28. Attempts to stimulate the activity of these uncharacterized, dormant methanogens by variation of conditions (temperature, pH and salinity) and substrates elicited a positive response at extreme salinity (4 M Na+), pH (9.5–10), elevated temperature (above 48–55°C) and in the presence of methylotrophic substrates together with formate or H2 (the combination used in the methyl-reducing pathway). The typical response involved a pronounced increase in methane production upon combining methyl compounds with formate or H2 (less active) compared to single substrates (Supplementary Figure 1 a). The mcrA profiling of such incubations revealed two distinct clusters closely related to the previously detected deep methanogenic lineage 28 (Supplementary Figure 2).

The same approach was used with sediment slurries from hypersaline lakes with neutral pH (with no previous evidence of the presence of methyl-reducing methanogens). In this case, enhanced methane production under methyl-reducing conditions (MeOH/trimethylamine + formate) was also observed at elevated temperatures (Supplementary Figure 1 b,c). The mcrA profiles indicated that typical halophilic methylotrophic methanogens (Methanohalophilus and Methanohalobium) were outcompeted at high temperature (50–60°C) by unknown, extremely halophilic methyl-reducers which formed a sister clade to the sequences from methyl-reducing incubations of soda lakes sediments in the mcrA tree (Supplementary Figure 2).

Cultivation of the extremely halophilic methyl-reducing methanogens

The active sediment incubations from hypersaline lakes (Supplementary Table 1) were used as an enriched source to obtain the methyl-reducing methanogens in laboratory culture using synthetic media with 2–4 M Na+, pH 7 (for salt lakes) or 9.5–10 (for soda lakes), supplemented with MeOH/formate or trimethylamine (TMA)/formate and incubated at 48–60°C. Methane formation was observed only at extreme salinity, close to saturation (4 M total Na+), but ceased after the original sediment inoculum was diluted by 2–3 consecutive 1:100 transfers. Addition of colloidal FeSxnH2O (soda lakes) or sterilized sediments (salt lakes), combined with filtration through 0.45 μm filters and antibiotic treatment, yielded a pure culture from Siberian soda lakes (strain AMET1 [Alkaliphilic Methylotrophic Thermophilic]), and 10 additional pure AMET cultures from hypersaline alkaline lakes in various geographic locations. A similar approach resulted in three highly enriched cultures at neutral pH from salt lakes (HMET [Halophilic Methylotrophic Thermophilic] cultures) (Supplementary Table 2). Phylogenetic analysis of the marker genes showed that AMET and HMET formed two potential genus-level groups that shared 90% 16S rRNA gene sequence identity.

Microbiological characteristics of the methyl-reducing methanogens

Cell morphology and composition

Both AMET and HMET possess small coccoid cells that are motile, in the case of AMET, and lack F420 autofluorescence that is typical of most methanogens. A thin, single-layer cell wall was present in both groups (Figure 1; Supplementary Figure 3). At salt concentration below 1.5 M total Na+, the cells lost integrity.

Fig. 1.

Fig. 1

Cell morphology of the methyl-reducing methanogens from hypersaline soda (strain AMET1, a–d) and salt (strain HMET1, e–f) lakes. a - phase contrast image; b and e - total electron microscopy images; c–d and f - electron microscopy images of thin sectioned cells. N - nucleoid; PHA? - a possible PHA storage granule; CPM - cytoplasmic membrane; ICPM - cell membrane invaginations; CW - cell wall. The light microscopy images are typical of 5–7 samples from 2 replicate cultures; the electron microscopy images are typical from technical replicates from the same culture (n=5 to n=10).

The extreme halophily of the discovered methanogens is unprecedented. The salt-tolerant methylotrophs isolated so far from hypersaline habitats, such as Methanohalobium, Methanohalophilus and Methanosalsum, all accumulate organic osmolytes (“salt-out” osmoprotection). In contrast, no recognizable organic osmolytes were detected in AMET1 cells that, instead, accumulated high intracellular concentrations of potassium [5.5 μmol/g protein or 2.2 M, assuming the cell density of 1.2 mg/ml for haloarchaea 29 and the measured protein content of 30%]. This concentration is twofold lower than that normally observed inside the cells of haloarchaea (12– 13 μmol/g protein) but close to that of Halanaerobium (6.3 μmol/g protein), both of which have been shown to employ the “salt-in” osmoprotection strategy 30,31. Furthermore, half of the sodium in the medium is present in the form of carbonates, which possess exactly twofold less osmotic activity than NaCl, resulting in decreased total osmotic pressure, and accordingly, a lower intracellular concentration of osmolytes in extreme natronophiles 32. This finding suggests that the extremely halophilic methyl-reducing methanogens rely on potassium as the major osmolyte.

The AMET cell pellets were pinkish in color, suggestive of the presence of cytochromes which was confirmed by difference spectra of a cell-free extract from AMET1 that showed peaks characteristic of b-type cytochromes (Supplementary Figure 4 a). Given that the cytochrome-containing methanogens of the order Methanosarcinales also synthesize the electron-transferring quinone analogue methanophenazine 33, we attempted to detect this compound in AMET1. Indeed, two yellow-colored autofluorescent hydrophobic fractions were recovered from the AMET1 cells, with main masses of 562 and 580 Da, which behaved similar to methanophenazine from Methanosarcina (mass 532 Da) upon chemical ionization (sequential cleavage of the 68 Da mass isoprene unit) (Supplementary Figure 4 b).

Growth physiology

Both AMET and HMET are methyl-reducing heterotrophic methanogens utilizing C1-methyl compounds as e-acceptor, formate or H2 as e-donor, and yeast extract or acetate as the C-source. Growth of both groups of organisms was stimulated by addition of external CoM (up to 0.1 mM). Despite the general metabolic similarity, the AMET cultures grew and survived long storage much better than the HMET cultures. The AMET cultures grew best with MeOH as acceptor and formate as donor (Figure 2a). Apart from MeOH, slower growth was also observed with methylamines and dimethylsulfide (Figure 2b). In sharp contrast to the known methyl-reducing methanogens, H2 was less effective as the electron donor.

Fig. 2.

Fig. 2

Growth and activity of methyl-reducing methanogens from hypersaline soda lakes. a - growth dynamics of strain AMET1 with MeOH+formate at 4 M total Na+, pH 9.5 and 50°C ( Ymax=1.5 mg protein/mM MeOH; μmax=0.012–0.015 h−1). b - methanogenic activity of washed cells of strain AMET1 grown with MeOH+formate (at 4 M total Na+, pH 9.5 and 48°C) with various methylated e-acceptors. c - influence of temperature on growth and activity of washed cells of various AMET strains at 4 M total Na+, pH 9.5 with MeOH+formate as substrate. d - influence of pH at 4 M Na+ on growth and activity of washed cells of strain AMET1 at 48°C with MeOH+formate as substrate. e - influence of salinity at pH 9.5 on growth and activity of washed cells of strain AMET1 with MeOH+formate as substrate. In all experiments, 100 μM hydrotroilite (FeS x nH2O) was added. Neither growth not activity were observed with a single substrate (i.e. methylated compounds, H2 or formate alone). VCH4 is a rate of methane formation, normalized either per culture volume in growth experiments or per biomass in cell suspension experiments. The error bars in 2a, 2b and 2d are SD of biological replicates (n=2). The plots in 2c and 2e represent results of a single sample analysis.

Both groups grew optimally around 50°C, with the upper limit at 60°C (Figure 2c, Supplementary Figure 5). The AMET isolates were obligate alkaliphiles, with optimum growth at pH 9.5–9.8 (Figure 2d), whereas the HMET cultures had an optimum at pH 6.8–7. The organisms of both groups showed the fastest growth and the highest activity at salt-saturating conditions, and thus qualified as extreme halo(natrono)philes (Figure 2e,f).

Effect of iron sulfides on growth and activity of AMET1

Apart from hydrotroilite (FeSxnH2O), AMET1 also grew, albeit less actively, in the presence of cristalline FeS, and yet less actively, with pyrite (FeS2). No other forms of reduced iron minerals tested (olivine, FeCO3, magnetite, ferrotine (FeSn) or various iron(II) silicates could replace FeS. Furthermore, methanogenic activity of resting cells depleted for FeS showed dependence on FeS addition (Figure 3). No methane was formed in the absence of either methyl acceptors or formate/H2, suggesting that Fe2+ likely served as a catalyst or regulator rather than a direct e-donor. The specific cause(s) of the dependence of AMET growth on iron (II) sulfides remains to be identified.

Fig. 3. Effect of hydrotroilite (FeS x nH2O) on growth and methanogenic activity of washed and exhausted cells of the AMET1 strain.

Fig. 3

Growth and incubation conditions: 4 M total Na+, pH 9.8, 48°C. Substrate: 50 mM CH3OH+50 mM formate. The culture was grown in the presence of sterile sand. The FeS-exhausted, washed cells were obtained by prolonged incubation with substrates without addition of FeS followed by washing and resuspension in a fresh buffer. The error bars are SD of biological replicates (n=3).

Comparative genomic analysis

General genome characteristics

The general genome characteristics of AMET1 and HMET1 are given in Table 1. Based on analysis of 218 core arCOGs 34, both genomes are nearly complete, with two genes missing from this list in AMET1 and three in HMET1. Two of these genes are missing in both genomes (prefoldin paralog GIM5 and deoxyhypusine synthase DYS1), suggesting that they were lost in the common ancestor (Supplementary Table 3). The presence of tRNAs for all amino acids is another indication of genome completeness. The high coverage of the AMET1 and HMET1 genomes by arCOGs implies that the unique phenotype of these organisms is supported largely by the already well-sampled part of the archaeal gene pool.

Table 1.

Summary statistics for the AMET1 and HMET1 genomes.

AMET1 HMET1
Number of contigs 8 4
Total length (base pairs) 1513137 2141311
Number of coding sequences 1514 2168
GC content 38% 35%
rRNAs 5S, 16S, 23S 5S, 16S, 23S
tRNAs (for different amino acids including pyrrolysine) 31 (21) 37 (21)
Proteins assigned to arCOGs 88% 79%
Completeness based on archaeal core arCOGs 99%# 99%#
CRISPR arrays 0 4
CRISPR-cas system subtypes - I-D, III-B
Transposon-related genes 4* 121*
Integrated elements (His2-like viruses) 3 2
*

Some are probably pseudogenes;

#

based on 218 core arCOGs

Phylogenetic analysis and taxonomy

A concatenated alignment of the 56 ribosomal proteins that are universally conserved in complete archaeal genomes 35 including AMET1 and HMET1 was used for maximum likelihood tree reconstruction (Figure 4a, Supplementary Table 3, Supplementary Data 1). Both AMET1 and HMET1 belong to a distinct clade, a sister taxon to the class Halobacteria, with 100% bootstrap support (Figure 4a). The 16S rRNA gene tree suggests that both organisms belong to the uncultured SA1 group that was first identified in the brine-seawater interface of the Shaban Deep in the Red Sea36 and subsequently in other hypersaline habitats37 (Supplementary Figure 6). According to the rRNA phylogeny, the group that includes AMET1 and HMET1 is well separated from the other classes in the phylum Euryarchaeota, both methanogenic and non-methanogenic. The 16S rRNA sequences of these organisms are equally distant from all classes in Euryarchaeota and fall within the range of recently recommended values (80–86%) for the class level classification 38. Together, these findings appear to justify classification of the SA1 group, including the AMET and HMET lineages, as a separate euryarchaeal class “Methanonatronarchaeia”. This class would be represented by two distinct genera and species “Methanonatronarchaeum thermophilum” (AMET) and ‘Candidatus Methanohalarchaeum thermophilum’ (HMET).

Fig. 4. Phylogenetic analysis of “Methanonatronarchaeia” (AMET1 and HMET1).

Fig. 4

The tree represents a phylogeny of archaea based on an alignment of concatenated ribosomal proteins. Methanogen clades are shown in blue and Halobacteriales in orange. The inferred methanogenic branches are highlighted in blue, the inferred loss of methanogenesis is indicated by dashed red branches. The arrow indicates the likely archaeal root. All branches are bootstrap-supported at 100% level. The original tree is available in Supplementary Data 1.

Comparative genomic analysis and reconstruction of main evolutionary events

Using arCOG assignments and the results of previous phylogenomic analysis 39, we reconstructed the major evolutionary events in the history of AMET1, HMET1 and Halobacteria (Figure 4a and Supplementary Table 4). This reconstruction indicates that evolution of the HMET1-AMET1 lineage was dominated by gene loss, whereas Halobacteria acquired most of their gene complement after the divergence from “Methanonatronarchaeia”. As shown previously, the common ancestor of Methanomicrobia and Halobacteria was a methanogen 39. The key genes coding for components of the protein complexes involved in the classical methanogenesis pathways, such as tetrahydromethanopterin S-methyltransferase (Mtr), F420-reducing hydrogenase and Ftr, appear to have been lost along the branch leading to the common ancestor of Halobacteria and “Methanonatronarchaeia”. After the divergence, Halobacteria continued to lose all other genes involved in methanogenesis and acquire genes for aerobic and mostly heterotrophic pathways, whereas “Methanonatronarchaeia” retained most pathways for anaerobic metabolism, while rewiring the methanogenic pathways for the mixotrophic lifestyle (Figure 5a). As in other cases, genome reduction in “Methanonatronarchaeia” affected RNA modification, DNA repair and stress response systems as well as surface protein structures 39. The subsequent gene loss occurred differentially in the two groups of “Methanonatronarchaeia”, suggesting adaptation to different ecological niches. The HMET group lost chemotaxis and motility genes and shows signs of adaptation to heterotrophy, whereas AMET retains the ability to synthesize most cellular building blocks at the expense of transporter loss. The AMET strains are motile but lost attachment pili, which are present in the vast majority of the species of the Halobacteria-Methanomicrobia clade 40, and many glycosyltransferases, suggesting simplification of the surface protein structures. The presence of two complete CRISPR-Cas systems in HMET1 compared to none in AMET1, along with the large excess of genes implicated in anti-parasite defense and transposons in HMET1 (Figure 5c and Table 1), further emphasize the lifestyle differences indicating that HMET1 is subject to a much stronger pressure from mobile elements than AMET1.

Fig. 5. Comparative genomic analysis and reconstruction of gene losses and gains.

Fig. 5

a. Reconstruction of gene loss and gain along in “Methanonatronarchaeia” (AMET1 and HMET1) and Halobacteriales. Light blue: arCOG complement; green: gains; dark blue: losses.

b. arCOG composition of AMET1 and HMET1.

c. Distribution of the differences in the arCOG composition of AMET1 and HMET1 by functional categories. For each category, the number of arCOGs unique to AMET1 and HMET1 is indicated. The functional classification of the COGs is described at ftp://ftp.ncbi.nih.gov/pub/wolf/COGs/arCOG/funclass.tab

d. Multidimensional scaling analysis of isoelectric point distributions. Orange: Halobacteria; green: halophilic archaea and bacteria; blue: other archaea and bacteria.

e. Multidimensional scaling analysis of genes enriched in methanogens.

Central metabolism reconstruction

In agreement with the experimental results, genome analysis allowed us to identify the genes of AMET1 and HMET1 that are implicated in energy flow and key reactions of biomass production, which appear to be simple and straightforward (Figure 6). The main path starts with utilization of C1 methyl-containing compounds for methane production by CoM methyltransferases and methyl-CoM reductase complexes, respectively. Similar to the methyl-reducing Methanomasillicoccales6, the genomes of AMET1 and, especially, HMET1 contains multiple operons encoding diverse methyltransferases (Supplementary Figure 7). Methyl-reduction is coupled with ATP generation and involves five membrane-associated complexes, namely, formate dehydrogenase, membrane-bound heterodisulfide reductase HdrED, Ni,Fe hydrogenase I, multisubunit Na+/H+ antiporter and H+ -transporting ATP synthase. The recently characterized complete biosynthetic pathway41 for coenzyme F430 is present in both genomes. In addition, membrane b-type cytochromes and methanophenazine-like compounds are implicated in electron transport.

Fig. 6. Reconstruction of the central metabolic pathways shared by “Methanonatronarchaeia”.

Fig. 6

The main methyl-reducing pathway is shown by thick magenta arrows. Metabolically fixed low molecular weight compounds are shown in green. Either gene name or respective arCOG number is shown for each reaction and shown in red (details are available at Supplementary Table 3). Final biosynthetic products are shown as follows: light blue for amino acids, pale yellow for nucleotides, brown for lipid components, pink for cofactors. Abbreviations: MF, methanofuran; H4MPT, tetrahydromethanopterin; CoM, coenzyme M, CoB – coenzyme B, CoA – coenzyme A.

Pyruvate, the key entry point for biomass production, is generated through acetate incorporation by acetyl-CoA synthetase (Figure 6). In a sharp contrast to most methanogens, both genomes lack genes for tetrahydromethanopterin S-methyltransferase Mtr complex and formylmethanofuran dehydrogenase Fwd complex, leaving all intermediate reactions, for which the genes are present, unconnected to other pathways (Figure 6). All four recently reported deep lineages of euryarchaeal methyl-reducing methanogens (Methanomasillilicoccales and ‘Candidatus Methanofastidiosa’) and those from the TACK superphylum (‘Candidatus Bathyarchaeota’ and (‘Candidatus Verstraetearchaeota’) 8,9 lack the Mtr and Fwd complexes as well, but they also lack all the genes involved in intermediate reactions. It is extremely unlikely that genes for all Mtr and Fdw complex subunits are present in both AMET1 and HMET1 but were missed by sequencing. Thus, these organisms might possess still unknown pathways to connect the intermediate reactions to the rest of the metabolic network.

In addition to the main biosynthetic pathway, AMET1 and HMET1 possess genes for three key reactions of anaplerotic CO2 fixation, namely, malic enzyme, phosphoenolpyruvate carboxylase and carbamoylphosphate synthase. Furthermore, complete gene sets for CO2 fixation pathway through archaeal RUBISCO are present in both genomes (Figure 6) 42. The great majority of the genes involved in the key biosynthetic pathways for amino acids, nucleotides, cofactors and lipids also were identified in both genomes and found to be highly expressed in proteomic analysis, as revealed by estimating the absolute protein amount based on the exponentially modified protein abundance index (emPAI) (Supplementary Table 6 and 7). Interestingly, emPAI-based abundances follow an exponential distribution in which 4 proteins involved in methanogenesis are among the 10 most highly expressed proteins.

HMET1 seems to be more metabolically versatile compared with AMET1, especially with respect to methanogenesis as well as amino acid and sugar metabolism (Figure 5b and 5c). However, unlike AMET1, HMET1 lacks several genes for cofactor biosynthesis, such as quinolinate synthase NadA and nicotinate-nucleotide pyrophosphorylase NadC, both involved in NAD biosynthesis; uroporphyrinogen-III decarboxylase HemE and protoporphyrinogen IX oxidase HemG involved in heme biosynthesis, sulfopyruvate decarboxylase involved in CoM biosynthesis and cofCED genes for the coenzyme F420 biosynthesis enzyme complex. This shortage of biosynthetic enzymes is consistent with experimental observations on poorer growth and survival of HMET in culture compared to AMET.

Adaptation to extreme salinity

Given that acidification of proteins is a common feature of the “salt-in” osmotic strategy, we estimated isoelectric points for the proteomes of a large representative set of halophilic and non-halophilic archaea and bacteria, and compared the distributions as described under Materials and Methods (Supplementary Table 5). The distributions of isoelectric points in the AMET1 and HMET1 proteomes are similar to those of moderately halophilic archaea and bacteria, with the notable exception of their closest relatives, the extremely halophilic Halobacteria, which form a distinct cloud of extremely acidic proteomes (Figure 5d). This separation indicates that the proteome acidity of Halobacteria dramatically changed after the divergence from “Methanonatronarchaeia” that appear to be an evolutionary intermediate on the path from methanogens to extreme halophiles. In agreement with the “salt-in” osmoprotection strategy, AMET1 and HMET1 encode a variety of K+ transporters (arCOG01960) but show no enrichment of transporters for known organic osmolytes, such as glycine, betaine, ectoine, or glycerol, compared with other archaea (Supplementary Table 3). On more general grounds, the “salt-out” strategy appears unlikely and perhaps unfeasible for extremely halophilic secondary anaerobes with relatively low energy yield. Taken together, these considerations suggest that the adaptation of “Methanonatronarchaeia” to the extreme salinity relies on the “salt-in” strategy. Whether these organisms possess additional mechanisms for cation-binding to compensate for the relatively low proteome acidity, remains to be determined, but it is also possible that the main counter-anion, in this case, is Cl.

Analysis of the AMET1 and HMET1 protein complements revealed a major expansion of the UspA family of stress response proteins with likely chaperonin function that could contribute to the structural stability of intracellular proteins (Supplementary Figure 8). Finally, we identified several arCOGs consisting of uncharacterized membrane proteins (eg. arCOG04755, arCOG04622, arCOG04619) that are specifically shared by AMET1, HMET1 and the majority of Halobacteria (Supplementary Table 3). Some of these proteins contain pleckstrin homology domains, which contribute to the mechanical stability of membranes in eukaryotes 43 and might play a similar role in “Methanonatronarchaeia”.

Notably, AMET1 protein expression analysis showed that the DNA/RNA-binding protein Alba, an archaeal histone and one of the UspA family proteins were among the ten most abundant proteins (Supplementary Table 6). These proteins contribute to RNA, DNA and protein stability and might play important roles in supporting growth under extreme salinity conditions.

Implications for the origin of methanogenesis

In previous phylogenetic analyses of the methyl coenzyme M reductase complex (McrABCD) subunits, the topology of the tree for these proteins generally reproduced the ribosomal protein-based phylogeny 13,22. In the present phylogenetic analysis that used different protein sets and methods, AMET1/HMET1, Methanomasilliicoccales 13, ANME1 group 44 and ‘Candidatus Methanofastidiosa’ (WSA2 group) 21 clustered together with high confidence (Supplementary Figure 9 and 10, Supplementary Data 2, 3 and 4). This topology differs from the topology of the ribosomal protein tree (Figure 4a). This discrepancy could result from a combination of multiple horizontal transfers of mcrABCD genes, differential gain and loss of paralogs, insufficient sampling of rare lineages, and phylogenetic artefacts caused by variation of evolutionary rates. Indeed, we observed a complex evolutionary history of McrA, including many lineage-specific duplications and losses (Supplementary Figure 9).

Reconstruction of evolutionary events and mapping the methanogens onto the archaeal tree suggests that the origin of methanogenesis dates back to the common ancestor of archaea, with multiple, independent losses in various clades (Figure 5a). The loss of the methanogenic pathways often proceeds through intermediate stages as clearly observed both in “Methanonatronarchaeia” and Methanomasilliicoccales (Figure 5a). Comparison of the gene sets (arCOGs) enriched in different groups of methanogens (Supplementary Table 3) using multidimensional scaling revealed distinct patterns of gene loss in “Methanonatronarchaeia”, Methanomasilliicoccales, ANME1 and ‘Candidatus Bathyarchaeota’, in agreement with the independent gene loss scenario (Figure 5e). Notwithstanding these arguments, the possibility that ‘Candidatus Bathyarchaeota’ and ANME1 acquired methanogenesis via HGT cannot be ruled out, relegating its origin to the common ancestor of Euryarchaeota. Further sampling of diverse archaeal genomes should resolve this issue.

Conclusions

We discovered an unknown, deep euryarchaeal lineage of moderately thermophilic and extremely halo(natrono)philic methanogens that thrive in hypersaline lakes. This group is not monophyletic with the other methanogens but forms a separate, class-level lineage “Methanonatronarchaeia” that is most closely related to Halobacteria. The “Methanonatronarchaeia” possess the methyl-reducing type of methanogenesis, where C1-methylated compounds serve as acceptor and formate or H2 are external electron donor, but differ from all other methanogens with this type of metabolism in the electron transport mechanism. In contrast to all previously described halophilic methanogens, “Methanonatronarchaeia” grow optimally in saturated salt brines and probably employ potassium-based osmoprotection, similar to extremely halophilic archaea and Halanaerobiales. This discovery is expected to have substantial impact on our understanding of biogeochemistry, ecology and evolution of the globally important microbial methanogenesis.

Methods

Samples

Anaerobic sediments (depth from 5 to 15 cm) and near bottom brines were obtained in hypersaline soda and salt lakes in south-western Siberia (Altai region) and south Russia Volgograd region and Crimea) in July of 2013–2015. The salt concentration varied from 100 to 400 g/l and the pH from 6.5–8 (salt lakes) to 9.8–10.5 (soda lakes). In addition, sediments from Wadi al Natrun alkaline hypersaline lakes in Egypt (October 2000) and alkaline hypersaline Searles Lake in California (April 2005) were used as inoculum in methanogenic enrichment cultures. The details of the lake properties are given in Supplementary Table 1. The methanogenic potential activity measurements followed by the mcrA analysis have been performed in 1:1 sediment-brine slurries as described previously 28.

Enrichment and cultivation conditions

For soda lakes, the sodium carbonate-based mineral media containing 1–4 M total Na+ strongly buffered at pH 10 28,45 was used for enrichments. For salt lakes, the mineral medium containing 4 M NaCl and 0.1 M KCl buffered with 50 mM K phosphates at pH 6.8 was employed. Both media after sterilization were supplied with 1 ml/l of acidic 46 and alkaline W/Se 47 trace metal solutions, 1 ml/l of vitamin mix 46, 4 mM NH4Cl, 20 mg/l yeast extract and 0.1 mM filter-sterilized CoM. The media were dispensed in serum bottles with butyl rubber stoppers of various capacity at 50 (H2) – 80% (formate) filled volumes, made anoxic with 5 cycles of argon flushing-evacuation and finally reduced by the addition of 1 mM Na2S and 1 drop/100 ml of 10% dithionite in 1 M NaHCO3. H2 was added on the top of argon atmosphere at 0.5 bar overpressure, formate and methanol − at 50 mM, methylamines − at 10 mM, methyl- and dimethyl sulfides − at 5 mM. In case of methyamines, ammonium was omitted from the basic medium. The incubation temperature varied from 30 to 65°C. Analyses of growth parameters, pH-salt profiling of growth and activity of washed cells, optical and electron microscopy and chemical analyses were performed as described previously 28,45.

Biomass composition

The presence of organic compatible solutes was tested by using HPLC and 1H-NMR after extraction from dry cells with EtOH and the intracellular potassium concentration was quantified by ICP-MS. The presence of the methanophenazine analogues was analyzed in aceton extract from lyophilized cells, followed by TLC separation, reextraction with MeOH-chloroform mixture and MS-MS spectrometry.

Genome sequencing and assembly

The genomic DNA from pure and highly enriched cultures was obtained by using UltraClean Microbial DNA Extraction Kit (MoBio Laboratories). The genome sequencing, assembly and automatic annotation of a pure culture from soda lakes and of a metagenome from a highly enriched salt lake culture was performed by BaseClear (Leiden, The Netherlands) using a combination of Illumina and PackBio platforms. Kmer tetranucleotide frequency analysis was used to identify contigs that are likely belong to HMET1 (meta)genome. Genome completeness has been estimated as described previously 48.

Genome annotation and sequence analysis

The final gene call has been combined from results by PROKKA 49 and GeneMarkS 50 pipelines. All protein-coding genes were assigned to the current archaeal Clusters of Orthologous Groups (arCOGs) as described previously 34. Protein annotations were obtained by a combination of arCOGs and PROKKA annotations and, in case of conflict, the respective protein have been manually reanalyzed using PSI-BLAST 51 and HHpred results 52 and their annotations were modified if necessary. Other genomes for comparative genome analysis were extracted from GenBank (March 2016), and where necessary, ORFs were predicted using GeneMarkS 50.

Protein sequences were aligned using MUSCLE 53. Alignments for the tree reconstruction have been filtered to obtain informative position as described previously 34. Approximate maximum likelihood phylogenetic trees were reconstructed using FastTree 54 and PHYML 55 methods. The PHYML program was used for the phylogenetic tree reconstruction from an alignment of 51 concatenated ribosomal proteins (287 species, 8072 positions), with the following parameters: LG matrix, gamma distributed site rates, default frequencies which were determined by PROTTEST program 56. Support values were estimated using an approximate Bayesian method implemented in PhyML. For McrA, multiple alignment (145 sequences and 553 positions) was used for tree reconstruction using PhyML and PROTTEST as described above.

Two sets of genes reconstructed previously using the program COUNT39, which employs a Markov chain gene birth and death model, for the ancestors of Halobacteriales Halobacteriales/Methanomicrobiales were used to infer gene gains and losses on the branches leading to Halobacteriales, and the discovered clade of extremely halophilic methanogens. We considered an arCOG to be present in these two clades when the respective COUNT probability was higher than 50%. Further reconstruction was done using a straightforward parsimony approach as explained in detail in Supplementary Table 4.

Isoelectric points (pI) of individual proteins were calculated according to Bjellqvist et al. 57 using the pK values from the EMBOSS suite 58. Genome-wide distributions of the protein pI were obtained as the probability density estimates at 100 points in the 2.0 – 14.0 pH range using the Gaussian kernel method 59. Kullback-Leibler divergence of the pI distributions for the pair of genomes A and B, DKL(A|B) was computed for all ordered pairs of the set. The distance between the genomes was estimated as D(A,B) = D(B,A) = (DKL(A|B) + DKL(B|A))/2 60. The matrix of genome distances was projected into a two-dimensional space using the Classical Multidimensional Scaling method 61,62 as implemented in the R package 63.

Proteomics

Proteomic analyses were conducted using the soda lake pure culture AMET1 (48°C, MeOH+formate) and the salt lake enrichment HMET1 (37°C, TMA+H2) (Supplementary Table 6 and 7). Cell pellets were dissolved in lysis buffer (8 M urea, 2 M thiourea, 5% CHAPS, 5 mM TCEP-HCl and a protease inhibitors cocktail). Homogenization of the cells was achieved by ultra-sonication for 5 min on ultrasonic bath. After homogenization, the lysed cells were centrifuged at 20,000×g for 10 min at 4 °C, and the supernatant containing the solubilized proteins was used for LC-MS/MS experiment. All samples were precipitated by methanol/chloroform method and re-suspended in a multi-chaotropic sample solution (7 M urea, 2 M thiourea, 100 mM TEAB; pH 7.5). Total protein concentration was determined using Pierce 660 nm protein assay (Thermo). 40 μg of protein from each sample were reduced with 2 μL of 50mM Tris(2-carboxyethyl) phosphine (TCEP, SCIEX), pH 8.0, at 37°C for 60 min and followed by 1 μL of 200mM cysteine-blocking reagent (methyl methanethiosulfonate (MMTS, Pierce) for 10 min at room temperature. Samples were diluted up to 140 μL to reduce urea concentration with 25mM TEAB. Digestions were initiated by adding 2 μg Pierce MS-grade trypsin (Thermo Scientific) to each sample in a ratio 1:20 (w/w), which were then incubated at 37°C overnight on a shaker. Sample digestions were evaporated to dryness in a vacuum concentrator and then desalted onto StageTip C18 Pipette tips (Thermo Scientific) until the mass spectrometric analysis.

A 1 μg aliquot of each sample was subjected to 1D-nano LC ESI-MSMS analysis using a nano liquid chromatography system (Eksigent Technologies nanoLC Ultra 1D plus, AB SCIEX, Foster City, CA) coupled to high speed Triple TOF 5600 mass spectrometer (SCIEX, Foster City, CA) with a Nanospray III source. The analytical column used was a silica-based reversed phase Acquity UPLC M-Class Peptide BEH C18 Column, 75 μm × 150 mm, 1.7 μm particle size and 130 Å pore size (Waters). The trap column was a C18 Acclaim PepMapTM 100 (Thermo Scientific), 100 μm × 2 cm, 5 μm particle diameter, 100 Å pore size, switched on-line with the analytical column. The loading pump delivered a solution of 0.1% formic acid in water at 2 μl/min. The nano-pump provided a flow-rate of 250 nl/min and was operated under gradient elution conditions. Peptides were separated using a 250 minutes gradient ranging from 2% to 90% mobile phase B (mobile phase A: 2% acetonitrile, 0.1% formic acid; mobile phase B: 100% acetonitrile, 0.1% formic acid). Injection volume was 5 μl.

Data acquisition was performed with a TripleTOF 5600 System (SCIEX, Foster City, CA). Data was acquired using an ionspray voltage floating (ISVF) 2300 V, curtain gas (CUR) 35, interface heater temperature (IHT) 150, ion source gas 1 (GS1) 25, declustering potential (DP) 100 V. All data was acquired using information-dependent acquisition (IDA) mode with Analyst TF 1.7 software (SCIEX, Foster City, CA). For IDA parameters, 0.25s MS survey scan in the mass range of 350–1250 Da were followed by 35 MS/MS scans of 100ms in the mass range of 100–1800 (total cycle time: 4 s). Switching criteria were set to ions greater than mass to charge ratio (m/z) 350 and smaller than m/z 1250 with charge state of 2–5 and an abundance threshold of more than 90 counts (cps). Former target ions were excluded for 15s. IDA rolling collision energy (CE) parameters script was used for automatically controlling the CE.

MS and MS/MS data obtained for individual samples were processed using Analyst® TF 1.7 Software (SCIEX). The reconstituted AMET1 and HMET1 chromosome sequence was used to generate the database for protein identification using the Mascot Server v. 2.5.1 (Matrix Science, London, UK). Search parameters were set as follows: carbamidomethyl (C) as fixed modification and acetyl (Protein N-term), Gln to pyro-Glu (N-term Q), Glu to pyro-Glu (N-term E) and methionine oxidation as variable modifications. Peptide mass tolerance was set to 25 ppm and 0.05 Da for fragment masses, also 2 missed cleavages were allowed. The confidence interval for protein identification was set to ≥ 95% (p<0.05) and only peptides with an individual ion score above the 1% False Discovery Rates (FDR) at PSM level were considered correctly identified. False Discovery Rates were manually calculated. The threshold of only one identified peptide per protein identification was used because FDR controlled experiments counter intuitively suffer from the two-peptide rule 64. To rank the protein abundance in each sample, the Exponentially Modified Protein Abundance Index (emPAI) was used in the present study as a relative quantitation score of the proteins in a complex mixture based on protein coverage by the peptide matches in a database search result 62. Although the emPAI is not as accurate as quantification using synthesized peptide standards, it is quite useful for obtaining a broad overview of proteome profiles.

Data availability

The final, assembled and annotated genomic sequences of the two isolates of “Methanonatronarchaeia” were deposited in GenBank under accession numbers: PRJNA356895 (AMET1) and PRJNA357090 (HMET1). Other data supporting the findings reported in this article are available from the Supplementary Information tables or from the corresponding authors upon request.

Supplementary Material

1

Acknowledgments

DYS was supported by STW (project 12226), Gravitation-SIAM Program (grant 24002002, Dutch Ministry of Education and Science) and by RFBR (grant 16-04-00035). KSM, YIW and EVK are supported by the intramural program of the U.S. Department of Health and Human Services (to the National Library of Medicine). The proteomic analysis was performed in the Proteomics Facility of The Spanish National Center for Biotechnology (CNB-CSIC) that belongs to ProteoRed, PRB2-ISCIII, supported by grant PT13/0001. This project has received funding from the European Union’s Horizon 2020 research and innovation program [Blue Growth: Unlocking the potential of Seas and Oceans] under grant agreement No [634486]. This work was further funded by grant BIO2014-54494-R from the Spanish Ministry of Economy, Industry and Competitiveness.

Footnotes

Author contributions. D.Y.S. performed the field work, the sediment activity incubations, enrichment and isolation of pure cultures and microbiological investigation of enriched and pure cultures. B.A. and A.Y.M. analyzed the mcrA and 16S rRNA gens in sediments and methanogenic cultures. M.F., P.N.G., S.C. and M.C.M. were responsible for the proteomic analysis. E.G. analyzed compatible solutes. K.S.M., Y.I.W. and E.V.K. performed genomic analysis and evolutionary reconstructions. D.Y.S., K.S.M. and E.V.K. wrote the paper. M.C.M.L. oversaw the project and participated in the data interpretation and discussion.

Competing interests. The authors declare no competing financial interests.

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Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

1

Data Availability Statement

The final, assembled and annotated genomic sequences of the two isolates of “Methanonatronarchaeia” were deposited in GenBank under accession numbers: PRJNA356895 (AMET1) and PRJNA357090 (HMET1). Other data supporting the findings reported in this article are available from the Supplementary Information tables or from the corresponding authors upon request.

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