BDGT and PDGT biosynthesis is mediated by a methyl transfer from a methionine intermediate.
Methylation of biomolecules is a common biochemical reaction typically catalyzed by methyltransferases or radical
S-adenosylmethionine (radical SAM) enzymes. Whether the reaction is catalyzed by a methyltransferase or a radical mechanism depends on the chemical reactivity of the substrate (
17). If an enzymatic methylation is responsible for the production of BDGTs and PDGTs, it would require activation of an inert
sp3 carbon, the methylene group located at the C-3 position of the glycerol backbone of GDGTs. Hence, a radical mechanism is most plausible. In lipid biosynthesis, such a radical methylation was shown to be responsible for the production of hopanoids methylated at their C-2 or C-3 position (
18,
19). Recently, two studies showed the involvement of radical SAM enzymes in the biosynthesis of GDGTs in
Sulfolobus acidocaldarius (
20,
21), and a radical mechanism was previously postulated for the lipid biosynthesis of
Methanothermobacter thermautotrophicus (
22,
23). A radical SAM-mediated methylation of GDGTs was thus suggested by Coffinet et al. (
11) to be involved in the biosynthesis of BDGTs and PDGTs, further supported by the presence of several radical SAM enzymes in the
M. luminyensis genome.
To test whether BDGTs and PDGTs derive from methylation(s) of GDGTs, a pure culture of
M. luminyensis was amended with [
methyl-
13C]methionine, the known precursor of radical SAM enzymes, and grown under optimal conditions (see details in Materials and Methods). A pure culture of
M. luminyensis was grown in parallel under identical conditions but without addition of any labeled substrate as a control batch. Core lipid distribution was determined by ultrahigh-performance liquid chromatography–high-resolution mass spectrometry (UHPLC-HRMS). Both cultures exhibited similar profiles in agreement with the lipid distribution previously published (
16).
13C-label incorporation was detected by inspection of the isotopologue distributions of GDGTs, BDGTs, and PDGTs (
Fig. 1), that is, the relative abundance of the molecular ions containing a different number of
13C atoms for each compound of interest recorded by HRMS analysis. Comparison of the isotopologue distribution between the labeled batch and the control batch (
Fig. 1) revealed incorporation of
13C in BDGT and PDGT molecular ions (
Fig. 1D to
G) during incubation with [
methyl-
13C]methionine, while GDGTs did not show any label incorporation (
Fig. 1B and
C). The isotopologue distribution observed for BDGTs (
Fig. 1D) was shifted by one unit, consistent with the transfer of one
13C-methyl carbon to one glycerol backbone of GDGTs to form BDGTs. The isotopologue distribution of PDGTs was shifted by two units, consistent with the addition of two
13C-methyl groups (
Fig. 1F).
Tandem mass spectrometry was performed to examine the position where the
13C-labeled methyl group(s) was added. In the BDGT molecule (
Fig. 2), incorporation of
13C was only observed in the isotopologue distribution of the butanetriol biphytanyl glycerol diether fragment (
Fig. 2C), confirming that the
13C-methyl group was selectively added at the backbone. Contrary to the structure of BDGTs, the PDGT structure remains putative. Initial elucidation of the structure was published by Zhu et al. (
12) based on tandem mass spectrometry analysis of a sediment sample from the Peru margin. MS
2 spectra of the PDGTs in the incubation with [
methyl-
13C]methionine, as well as in the unlabeled control incubation (Fig. SA1 in the supplemental material), revealed diverging patterns compared to the original MS
2 spectrum (
12). Notably, absence of a fragment at
m/z 1228 and presence of a fragment at
m/z 1243 with an isotopologue distribution centered at the [M+1] ion in the incubation with [
methyl-
13C]methionine suggest an alternative structure for PDGTs where one methyl group would be added to each of the two lipid backbones instead of two methyl groups to the same glycerol moiety as previously hypothesized for PDGTs found in environmental samples (
12) (Fig. SA1). To date, in environmental samples, as well as in
M. luminyensis, concentration of PDGTs was too low to confirm these putative structures by NMR analysis. If this alternative structure were to be confirmed, the name of the lipid with an exact mass of 1,329.3467 Da in the
M. luminyensis lipidome would have to be modified to butanetriol dibiphytanyl butanetriol tetraether (BDBT). In any case, the specific incorporation of methyl group(s) at the backbone(s) position observed in the present incubation provides direct evidence that BDGT and the putative PDGT compounds result from an enzymatic methylation of the common archaeal GDGT lipid, conceivably performed by a radical SAM enzyme.
The ability to produce BDGTs and PDGTs has, so far, only been observed in
M. luminyensis; Becker et al. (
16) suggested these lipids may be specific to the order
Methanomassiliicoccales after screening 25 archaeal strains representing several archaeal phyla. In this study, we analyzed the lipid composition of another
Methanomassiliicoccales representative, “
Candidatus Methanogranum gryphiswaldense,” enriched from peat soil (
24,
25) (see supplementary methods for details of the enrichment procedure). Absence of BDGTs and PDGTs in this enrichment was revealed by analysis of the acid-hydrolyzed lipid extract of its biomass (Fig. SA2). Interestingly, “
Ca. Methanogranum gryphiswaldense” belongs to the family
Methanomethylophilaceae, while
M. luminyensis belongs to the family
Methanomassiliicoccaceae. We therefore suggest that the radical SAM enzyme(s) responsible must be restricted to a limited number of archaeal taxa, including the family
Methanomassiliicoccaceae.
An extended bioinformatics search relative to our previous paper (
11) of the
M. luminyensis genome for the radical SAM motif (protein family [Pfam] identifier pfam04055 and close homologs) identified 37 putative radical SAM enzymes. To further discriminate which gene could be responsible for backbone methylation of GDGTs, we performed a BLASTP search of these 37 proteins in the genomes of “
Ca. Methanogranum gryphiswaldense” (
25), as well as of the 25 strains previously shown to be devoid of BDGTs and PDGTs (
16) (Fig. SA3). Seven radical SAM enzymes identified in
M. luminyensis were found to share little homology, based on their E values, with proteins from the other 26 strains and are likely candidates to perform the backbone methylation (Table SA1). Interestingly, a BLASTP search of these seven proteins against the National Center for Biotechnology Information (NCBI) non-redundant protein sequence database revealed close homologues in genomes of some methanogenic archaea and anaerobic methane-oxidizing archaea and with members of “
Candidatus Bathyarchaeaota” phylum (Fig. SA4). This phylogenetic distribution is in agreement with the BDGT distribution and isotopic composition observed in environmental samples so far (
11,
13). Notably, Meador et al. (
13) suggested, on the basis of the BDGT abundance patterns in relation to bathyarchaeotal 16S genes in sediment samples, that members of “
Candidatus Bathyarchaeaota” are candidates for their production. This preliminary bioinformatic analysis will have to be complemented by microbial genetics once the genetic manipulation of a BDGT-producing microorganism has been developed.
Backbone methylation index as a potential proxy for energetic status and activity of microbial communities in the environment.
M. luminyensis biomass was harvested at two time points in the course of the incubation, during the exponential phase and during the stationary phase (
Fig. 3A and
B). An increase in the relative abundance of BDGTs and PDGTs in the stationary phase was observed in incubations with and without label addition (Table SA2). In the present incubations, we observed a decrease in the concentration of both the major carbon (acetate) and energy (methanol) sources (
26) of
M. luminyensis (Fig. SA5). This suggests that additional methylation of the membrane lipid backbone might be a response to limitation in energy or carbon substrate availability. Previous studies reported modification of the membrane lipid structures when energy or/and nutrients were scarce, notably via methylation mechanisms. For example, a methylation reaction converts
cis-unsaturated fatty acids to cyclopropane derivatives in many bacteria once they reach the stationary growth phase (
27). In the archaeal realm, studies on cultured species from the euryarchaeal, crenarchaeal, and thaumarchaeal phyla showed that the degree of cyclization of GDGTs was increasing when nutrient availability and/or energy supply were limited (
2–4). However, secondary processes, in particular, pH modification, could also influence the lipid distribution in the membrane and cannot be ruled out at the moment. Other variables whose impact on the lipid distribution are currently not well understood, such as accumulation of metabolic waste products in batch experiments, could also warrant further investigation. Dedicated experiments using continuous cultivation in a chemostat could help to further constrain the environmental parameter(s) that are triggering backbone methylation (
2,
4).
Nevertheless, the substantial increase of methylated lipids observed in the stationary phase indicates a metabolic response to a change in the growth status of
M. luminyensis that possibly could also be observed in sediments. We thus introduced the backbone methylation index (BMI) to express the change in methylation degree with change of growth status; the BMI corresponds to the relative proportion of PDGTs as fraction of the sum of BDGTs and PDGTs [PDGTs/(BDGTs + PDGTs)] (
Fig. 3C). GDGTs were not included in the calculation because of their highly diverse sources in marine sediments (
28), which would reduce the sensitivity to detecting responses of BDGT- and PDGT-producing archaea. BMI was then assessed in a set of marine sediment samples collected in the Mediterranean Sea that were previously investigated for their BDGT and PDGT content (
11). An obvious variable that could affect BMI is sediment age because, with increasing age, the rate of microbial decomposition of organic matter decreases (
29), and the proportion of microbial cells in stationary phase or dormancy increases (
30). Indeed, BMI increases with the estimated age of the sediment (
Fig. 4). The observed higher ratios of backbone methylation in the oldest, most energy-deprived sediment samples are therefore generally consistent with the hypothesis derived from our laboratory observations. Based on these preliminary observations in pure cultures and sediment samples, we propose that the herein introduced backbone methylation index could be used in natural settings to explore energetic status and growth activity of microbial communities along environmental gradients. Backbone methylation could serve to reduce membrane permeability to limit energy loss or could enhance the intact polar lipid stability, thus reducing maintenance energy requirements. To fully understand the environmental triggers and cellular processes responsible for backbone methylations will require further research, but this work opens new research avenues, notably for studies of the deep sedimentary biosphere.