Research Article | Open Access
Lena Kröninger, Jacqueline Gottschling, Uwe Deppenmeier, "Growth Characteristics of Methanomassiliicoccus luminyensis and Expression of Methyltransferase Encoding Genes", Archaea, vol. 2017, Article ID 2756573, 12 pages, 2017. https://doi.org/10.1155/2017/2756573
Growth Characteristics of Methanomassiliicoccus luminyensis and Expression of Methyltransferase Encoding Genes
DNA sequence analysis of the human gut revealed the presence a seventh order of methanogens referred to as Methanomassiliicoccales. Methanomassiliicoccus luminyensis is the only member of this order that grows in pure culture. Here, we show that the organism has a doubling time of 1.8 d with methanol + H2 and a growth yield of 2.4 g dry weight/mol CH4. M. luminyensis also uses methylamines + H2 (monomethylamine, dimethylamine, and trimethylamine) with doubling times of 2.1–2.3 d. Similar cell yields were obtained with equimolar concentrations of methanol and methylamines with respect to their methyl group contents. The transcript levels of genes encoding proteins involved in substrate utilization indicated increased amounts of mRNA from the mtaBC2 gene cluster in methanol-grown cells. When methylamines were used as substrates, mRNA of the mtb/mtt operon and of the mtmBC1 cluster were found in high abundance. The transcript level of mtaC2 was almost identical in methanol- and methylamine-grown cells, indicating that genes for methanol utilization were constitutively expressed in high amounts. The same observation was made with resting cells where methanol always yielded the highest CH4 production rate independently from the growth substrate. Hence, M. luminyensis is adapted to habitats that provide methanol + H2 as substrates.
Among living organisms, methane formation is restricted to methanogenic organisms of the domain Archaea. These organisms are important players of the global carbon cycle due to their capability to use fermentation products of organic matter as substrates . While methanogenic archaea have been studied extensively with respect to biogas production and other man-made habitats, little is known about human-associated methanogens . One of these organisms is Methanomassiliicoccus luminyensis, which was originally isolated from human feces . This organism is the only member of the seventh order of methanogens, the Methanomassiliicoccales, that is available in pure culture. DNA sequence analysis indicated that members of the Methanomassiliicoccales are also found in gastrointestinal tracts of higher termites and millipedes, the digestive tracts of animals, rice paddy fields, natural wetlands, subseafloor and freshwater sediments [4, 5] and in anaerobic digester sludge . These findings highlight the wide distribution and diversity of members of the order Methanomassiliicoccales which are phylogenetically related to the Thermoplasmatales but only distantly related to other methanogens [4, 7].
Methanogenic archaea are usually divided into three major groups based on their substrate spectrum. While hydrogenotrophic archaea use H2 + CO2 or formate as substrates, methylotrophic organisms form methane from methylated compounds, and aceticlastic archaea use acetate as substrate . M. luminyensis is distinct from these common groups because it uses H2 as electron donor but is not able to reduce CO2 to CH4 . In the first description of the strain, it was stated that methanogenesis is possible by methanol reduction with H2 as the electron donor . In this respect, M. luminyensis resembled Methanosphaera stadtmanae, another methanogenic archaeon that was isolated from human feces and can use methanol in the presence of H2 [9, 10]. Genome analysis revealed that besides the genes for methanol utilization, members of the genus Methanomassiliicoccus contain complete sets of genes for the degradation of methylamines to CH4 and NH3 [5, 11, 12]. Lang et al.  showed that methane accumulated in the culture headspace of M. luminyensis containing methanol, monomethylamine (MMA), dimethylamine (DMA), or trimethylamine (TMA) in the presence of H2. In addition, it was found that M. luminyensis grows on TMA in the presence of H2 but not on TMA in the absence of H2 [13, 14]. Due to the ability to use TMA as substrate, M. luminyensis is also discussed in the context of the so-called “Archaebiotics” [2, 14]. These therapeutic agents were proposed as a treatment for patients suffering from trimethylaminuria. The patients hold a genetic disposition that prevents oxidation of TMA to trimethylamine oxide (TMAO) in the human liver. TMA is a product of degradation processes in the human gut and can be spread throughout the body by being absorbed from the intestinal lumen and transferred into the bloodstream. When the mechanism to oxidize TMA to TMAO is absent, TMA rapidly accumulates and results in a fish-like odor coming from patients’ sweat and breath . The cultivation of M. luminyensis in the intestines of patients and the simultaneous metabolization of TMA could reduce the accumulation of TMA in the intestines and could prevent the fish-like odor .
Another aspect of “Archaebiotics” based on M. luminyensis is the general conversion of TMA into TMAO in the human body. TMAO is thought to raise the risk for developing cardiovascular diseases, for example, arteriosclerosis. Therefore, a low TMAO level is generally desirable in healthy individuals. Due to the fact that M. luminyensis produces methane from TMA and TMA oxidation to TMAO does not take place, the occurrence of this archaeon in the human intestinal tract could decrease accumulation of TMAO and consequently the risk for cardiovascular diseases caused by this compound .
The metabolism of M. luminyensis and members of the Methanomassiliicoccales is unique from other methanogenic archaea because they cannot be classed into the typical methanogenic groups (hydrogenotrophic, aceticlastic, and methylotrophic methanogenic archaea). In fact, M. luminyensis is a hybrid of the common methanogenic groups with respect to its mode of energy conservation [11, 12]. When methylated compounds are metabolized by M. luminyensis, the methyl group is first transferred by substrate-specific methyltransferases to 2-mercaptoethanol (HS-CoM). In this process, methyl-CoM is formed which is then reduced to methane by the methyl-CoM reductase with 7-mercaptoheptanoyl-threonine phosphate (HS-CoB) as electron donor. This reaction leads to the formation of the heterodisulfide CoM-S-S-CoB. The reduction mechanism of CoM-S-S-CoB to HS-CoM and HS-CoB is not completely resolved in M. luminyensis, yet. It is assumed that in the course of the degradation of two molecules of methanol to methane, two molecules of heterodisulfide are formed [11, 12]. One of the heterodisulfide molecules is reduced by a multienzyme complex consisting of a [NiFe] hydrogenase (Mvh) and a heterodisulfide reductase (HdrABC), which uses H2 as electron donor and transfers electrons to heterodisulfide and ferredoxin (Fd) in a bifurcation reaction. It was suggested that Fdred can then be oxidized by a membrane-bound dehydrogenase (Fpo complex), which is similar to the H+-translocating NADH dehydrogenase (complex 1) found in the respiratory chain of eukaryotes and many bacteria. In M. luminyensis, a second heterodisulfide reductase (HdrD) serves as electron-accepting unit and reduces the second heterodisulfide molecule [11, 12]. During Fdred oxidation and simultaneous heterodisulfide reduction, protons can be translocated across the membrane to establish an electrochemical gradient, which is needed for ATP synthesis.
Because of the importance of M. luminyensis with respect to the human gut microbiome and its interesting mode of CH4 formation, it is essential to analyze the physiology and biochemistry of this organism. Here, we present data on the growth behavior and gene expression of M. luminyensis for the development of methods that permit efficient growth and allow the production of sufficient cell mass for further biochemical analysis of the metabolism of this organism.
2. Materials and Methods
2.1. Strains and Culture Conditions
M. luminyensis DSM 25720 was obtained from the Deutsche Sammlung für Mikroorganismen und Zellkulturen (Braunschweig, Germany). Cultures (50 or 500 mL) were grown in complex medium as described by Hippe et al.  under a hydrogen atmosphere (200 kPa). Methanol, MMA, DMA, and TMA were added prior to inoculation as indicated from sterile stock solutions. Na2S (0.3 g/L) and cysteine (0.9 g/L) were added as reducing agents. Ampicillin (100 μg/mL) and tetracycline (10 μg/mL) were applied to ensure culture purity. Cells were grown at 37°C without agitation, and growth was monitored by measuring the optical density at 600 nm.
2.2. Quantification of CH4, Methanol, MMA, DMA, TMA, and Acetate
CH4 and methanol contents were quantified using gas chromatography (GC), respectively. For CH4 quantification, 25 μL samples were taken from the headspace of the cultures and injected into a GC (PerkinElmer Clarus® 480, Rascon FFAP column 25 m × 0.25 micron, PerkinElmer, Waltham, USA) with a flame ionization detector (FID). Measurements were conducted at a column temperature of 120°C, an injector temperature of 150°C, and a detector temperature of 250°C. N2 was used as carrier gas. A CH4 standard with a defined concentration of 10% (90% argon) was used as reference and was measured prior to and during measurement series.
For methanol quantification, 1 μL samples from culture supernatants were injected into a GC (Shimadzu GC-14A, Shimadzu, Duisburg, Germany with Agilent Chromosorb 101 column, Agilent Technologies, Santa Clara, USA) with a column temperature of 100°C, an injector temperature of 220°C and a detector temperature of 220°C with N2 as carrier gas. The methanol content in the culture supernatants was quantified by correlation to a methanol standard curve.
For MMA, DMA, and TMA quantification, the cells were separated from the medium by centrifugation. To remove Na2S from the samples, the supernatant was mixed with H2O2 (0.3% (v/v) final concentration). The precipitate was removed by centrifugation (20,000 ×g, 1 min), and the cleared supernatant was used for methylamine quantification. All further steps were performed as described by Krätzer et al. . Acetate was quantified by HPLC on an Aminex HPX-87H (BioRad, Munich, Germany, 300 mm × 7.8 mm) column at 25°C. 5 mM H2SO4 was used as eluent, and a flow rate of 0.3 mL/min was applied. Samples were prepared by adding 300 μL 5 mM H2SO4 to 300 μL of the culture supernatant. The samples were centrifuged to remove precipitates and were filtered. 20 μL of the mixture was then applied to HPLC. Standard curves were prepared for all compounds from 0 to 50 mM concentrations.
2.3. Determination of Dry Weight
For dry weight determination, 500 mL cultures of M. luminyensis were inoculated as mentioned above. At each time point, the optical density was recorded and 50 mL samples were withdrawn from the culture. The cells were harvested and washed by centrifugation (6000 ×g, 20 min, 10°C). The pellets were dried at 70°C and weighed after two days.
Total RNA from M. luminyensis was obtained from 500 mL cultures grown to mid exponential phase on 150 mM methanol + H2, 50 mM TMA + H2, 75 mM MMA + H2, or 75 mM DMA + H2. Cells were harvested by centrifugation (11,000 ×g, 15 min, 4°C) and resuspended in 3 mL TRI reagent (Sigma-Aldrich, Steinheim, Germany) for RNA stabilization and cell lysis. RNA was extracted using 1-bromo-3-chloropropane and was purified by RNA Clean & Concentrator™-5 kit (Zymo Research, Freiburg, Germany). DNAse I was applied to RNA samples to remove DNA contaminations. RNA concentration and purity were determined spectrophotometrically using a BioSpectrometer® according to a standard protocol (Eppendorf, Hamburg, Germany). Control PCR experiments confirmed that the RNA samples did not contain DNA contaminations. The primer sequences that target genes coding for substrate-specific corrinoid proteins are shown in Table 1. Homologous genes were aligned using the program Clustal Omega , and regions showing maximal differences were chosen for primer generation. The ribosomal S15 gene (WP_026068997) was used as reference gene. To analyze cross-hybridization between highly homologous corrinoid protein-encoding genes, we checked annealing of primer combinations of different homologous genes under real-time PCR conditions using chromosomal DNA as templates. It came out that only combinations of specific forward and reverse primers designed for each gene were efficient in PCR and in qRT-PCR, indicating that there was no significant cross-annealing between homologous genes. qRT-PCR reactions were performed using a qRT-PCR Green Mix One Step Kit (biotechrabbit, Hennigsdorf, Germany) which is based on SYBR Green as fluorescence dye. To each PCR reaction, 150–200 ng RNA was applied and a negative control without reverse transcriptase was carried along to verify that DNA contaminations did not affect the results. To perform the PCR steps and to measure fluorescence, the cycler CFX Connect™ and a suitable software (BioRad, Munich, Germany) were used. The PCR fragments resulted in a single peak in the melting curve analysis, respectively. For calculations of ΔCt values, the quantification cycle (Ct) of the reference gene (ribosomal protein 15S) was subtracted from the Ct value of each gene of interest. The fold change of each gene was calculated using the formula 2−ΔCt.
2.5. Preparation of Resting Cells
Resting cells were prepared from cultures grown on 150 mM methanol + H2 or 50 mM TMA + H2 as described above. Cultures were grown to mid log phase (OD600 0.1-0.2) and harvested by centrifugation (11,000 ×g, 15 min, 10°C). The cell pellets were washed twice using stabilization buffer (17 mM NaCl, 7 mM KCl, 2 mM MgCl2 × 6 H2O, 1 mM CaCl2 × 2 H2O, 6 mM NH4Cl, 1.5 mM KH2PO4, 1 mM Na2SO4, 20 mM BisTris, and 200 mM sucrose and pH 7.4) and finally resuspended in stabilization buffer. 2 mL of the resting cell suspension was filled into a 9 mL rubber stoppered glass vial flushed with H2. Cells were equilibrated at 37°C and 200 rpm for 5 min. Methane production was initiated by the addition of a methyl group donor (75 mM methanol, 75 mM MMA, 37.5 mM DMA, or 25 mM TMA) from anaerobic stock solutions. During the experiment, the cells were incubated at 37°C and 200 rpm. Samples from the headspace (25 μL) were taken at different time points and analyzed by gas chromatography as described above to monitor CH4 production.
3.1. Growth on Methanol
There is still very little known about the physiology and biochemistry of members of the order Methanomassiliicoccales and the enzymes, which are involved in the methanogenic pathway. Since the methanol concentration for optimal growth of M. luminyensis was not analyzed in detail yet, the organism was grown in complex media containing different amounts of methanol under a H2 atmosphere (200 kPa). Growth of the cells was examined after addition of 20, 40, 60, or 80 mM methanol (Figure 1). Samples from the culture medium were used to analyze optical density, cell dry weight, and methanol concentration. All cultures showed a lag phase of about 2 d followed by an exponential phase of 5–10 d depending on the methanol content. The growth rate of 0.38 ± 0.04 d−1 was almost identical in all cultures independently from the amount of methanol that was added (Figure 1(a)). The corresponding doubling time (td) was 1.8 ± 0.2 d. Gas chromatographic analysis of the culture supernatant indicated an exponential increase in methanol consumption that directly correlated with the optical density. Methanol was almost completely consumed at the beginning of the stationary growth phase (not shown). The time point of substrate exhaustion depended on the methanol concentration at the beginning of the experiment. Hence, growth of the cells stopped after 6.5 d (20 mM methanol), 8 days (40 mM methanol), 9.5 d (60 mM methanol), and 12 d (80 mM methanol), respectively (Figure 1(a)). Further evidence that substrate utilization was directly coupled to the increase of cell mass of the cultures resulted from the correlation of methanol consumption and optical density in the course of the exponential growth phase (Figure 1(b)). From the slope of the curve, it was calculated that M. luminyensis had to convert 24 ± 2 mM methanol to reach an optical density of 0.1. In addition, it became evident that there was a linear correlation between optical density and dry weight (optical density of 1 = 0.59 g dry weight/L; Figure 1(b), inset). From these data, a growth yield of 2.4 g dry weight/mol methanol could be calculated.
Methanol consumption and methane formation were not measured simultaneously, yet. To check the stoichiometry, M. luminyensis was grown under a H2 atmosphere at 37°C in complex medium containing 150 mM methanol. Samples from the gas phase were frequently taken to quantify the methane content in the headspace. Furthermore, samples from the culture medium were used to analyze the methanol concentration. It was found that 150 mM methanol was degraded within 25 d and equimolar amounts of CH4 were formed (Figure 2). All samples taken from different cultures and at different time points indicated that methanol and methane were formed in a ratio of 0.98 ± 0.2. The doubling time during growth on 150 mM methanol was 1.9 ± 0.1 days. Additionally, the methane production rate (mmol CH4 L culture−1 d−1) of the cultures was analyzed. The rate strongly correlated with the optical density and the growth phase of the cultures. The highest methane production rate was observed at the end of the exponential phase and reached a value of 14 mmol CH4 L culture−1 d−1 (not shown). Once the stationary phase was reached (day 10), the methane production rate decreased sharply and in the end, CH4 formation almost stopped completely. Interestingly, methanol was not the limiting growth factor because the stationary phase started (day 10) before methanol was completely utilized. A detailed analysis revealed that the cultures reached a maximal optical density of 0.5 and degraded only about 110 mM methanol in the course of the exponential phase (more details are shown in Figure S available online at https://doi.org/10.1155/2017/2756573). The remaining substrate was slowly consumed over one week during stationary phase without further cell growth (Figure 2). H2 was not a limiting factor since this gas was always added in exceeding amounts by gassing the cultures after each sampling. In addition, the separate addition of double amounts of salts, acetate, vitamins, trace elements (including tungsten and selenite ), iron ions, amino acids, yeast extract, or yeast/peptone did not result in an increase of the optical density. Furthermore, the complementation of media with rumen fluid, fluid from biogas plant sludge, cell-free extracts from Methanosarcina mazei or Methanotorris igneus, or short-chain fatty acids had no effect on the growth efficiency. Hence, the reason why growth of M. luminyensis stopped after the consumption of about 110 mM methanol is unknown.
We also tested whether acetate as component of the complex medium could be used as carbon source. HPLC analysis of cell-free culture supernatant indicated that the acetate concentration decreased from 10.2 mM to 5.5 mM in the course of the exponential phase (Figure 2). A detailed analysis of acetate degradation and cell growth indicated that 16.5 ± 2 mmol acetate (or 33 mmol carbon atoms) was consumed for the formation of 1 g dry weight (Figure S). Assuming that the dry mass of M. luminyensis contains 47% carbon , the total amount of carbon sums up to 39.2 mmol per g dry weight. Hence, about 84% of cellular carbon derived from acetate.
3.2. Growth on Methylamines
To analyze methylamine degradation in detail, M. luminyensis was cultured in complex medium containing different methylamines under a H2 atmosphere (200 kPa) and several growth parameters were determined (Figure 3). 75 mM MMA was completely degraded in the presence of H2 in the headspace of the cultures within 18 d (Figure 3(a)). The utilization of MMA coincided with the increase of the optical density. The final optical density of 0.3 was in the same range as with 75 mM methanol as substrate. The doubling time in the exponential phase was 2.3 ± 0.5 d and was longer in comparison to growth on methanol. MMA was almost entirely consumed at the end of the exponential phase.
To investigate growth of M. luminyensis on DMA, the organism was grown in the presence of 37.5 mM DMA + H2 and the optical density, as well as the DMA concentration in the medium were monitored over time (Figure 3(b)). DMA possesses two methyl groups for methanogenesis. Therefore, only half of the DMA concentration was needed in comparison to MMA or methanol to obtain the same growth yield. After inoculation of the medium, DMA was successively degraded while the optical density of the culture increased simultaneously. The cells grew with a growth rate of 0.32 ± 0.07 d−1 and a doubling time of 2.2 ± 0.5 d. When DMA was completely consumed, the organism stopped growing and merged into stationary phase (Figure 3(b)). At this time point, the optical density reached 0.28 which was in good agreement with the final optical density obtained with 75 mM MMA + H2.
TMA contains three methyl groups, which are sequentially converted into methane in Methanosarcina species [17, 20]. Hence, DMA and MMA are possible intermediates of TMA degradation and could accumulate in the medium. To investigate TMA utilization in M. luminyensis, substrate consumption, product formation, and growth parameters were analyzed (Figure 3(c)). The TMA concentration decreased continuously until almost all substrate molecules were consumed. The final optical density of cultures grown on 25 mM TMA was 0.28. This value was in the same range of the final optical densities of cultures grown on 75 mM methanol or 75 mM MMA, respectively. Due to the fact that TMA possesses three methyl groups, a TMA concentration of 25 mM equals a MMA (or methanol) concentration of 75 mM with respect to the amount of methyl group equivalents per substrate molecule. TMA-degrading cultures showed a doubling time of 2.1 ± 0.4 d which was the fastest growth rate observed for methylamines. Interestingly, at the beginning of the exponential growth phase, significant concentrations of DMA could be detected in the culture supernatants reaching concentrations of up to 4 mM. In the late exponential phase, the entire amount of DMA was consumed (Figure 3(c)). In contrast to Ms. mazei , M. luminyensis did not form extracellular MMA as an intermediate of methanogenesis from TMA. To analyze the efficiency of the energy conserving system of M. luminyensis grown on TMA in comparison to methanol, the growth yield was determined for cultures growing on TMA. Interestingly, the same growth yield of 2.4 g dry weight/mol CH4 was determined for TMA and methanol suggesting that both substrates are equally suitable substrates for the overall metabolism.
3.3. Analysis of the Transcript Level of Genes Encoding Enzymes Involved in Substrate Demethylation
Methylated C1 substrates are channeled into the methylotrophic pathway of methanogenesis by substrate-specific methyltransferases . To analyze which genes are involved in consumption of methanol or the three methylamines, qRT-PCR experiments were performed using gene-specific primers and RNA preparations from M. luminyensis cultures grown on the respective substrate and harvested in the mid log phase. Primers were designed for the specific amplification of transcripts from nine different genes encoding corrinoid-containing methyl-accepting proteins which are predicted to participate in methyl group transfer from the substrates to HS-CoM. These corrinoid proteins are substrate specific and are referred to as MtaC, MttC, MtbC, and MtmC for the breakdown of methanol, TMA, DMA, and MMA, respectively. The corresponding genes are found on the chromosome of M. luminyensis in one to four copies [7, 12]. Single genes are present for TMA (mttC) and DMA (mtbC) utilization, respectively. The corrinoid protein involved in methanol consumption is encoded by three different genes (mtaC1, mtaC2, and mtaC3). Four copies of the gene mtmC (mtmC1, mtmC2, mtmC3, and mtmC4) were detected encoding the corrinoid protein MtmC for MMA degradation. In addition, primers were generated for the gene encoding the ribosomal subunit S15 which was used as a reference in the qRT-PCR studies to determine expression levels. It is most likely that this gene is highly expressed during the exponential growth phase. The qRT-PCR results indicated different transcription patterns when the cells were grown on methanol and methylamines, respectively (Figures 4 and 5). During growth on methanol, the gene mtaC2 showed a 15-fold higher mRNA concentrations in comparison to the reference gene encoding the ribosomal protein S15, indicating the importance of the corresponding corrinoid protein for methanol metabolism (Figure 4). In contrast, mtaC1 and mtaC3 were transcribed at low levels with 10- to 50-fold lower transcript abundance in comparison to the reference gene. The close association of mtaB and mtaC genes in the genome suggests that they form transcription units as in other methanogens [17, 22]. Hence, the results indicate that methyl group transfer from methanol is mainly performed by the corrinoid protein MtaC2 in connection with the methyltransferase MtaB2. Gene transcripts encoding corrinoid proteins for methylamine utilization (mttC, mtbC, and mtmC1–C4) were only found in low amounts during methanogenesis from methanol (Supplementary Table available online at https://doi.org/10.1155/2017/2756573). This expression pattern considerably changed during growth on TMA. The genes mttC and mtbC revealed a 75- and 200-fold higher expression value in TMA-grown cells compared to cells grown on methanol, respectively (Figure 5(a)). Therefore, the corresponding corrinoid proteins together with their partners MttB and MtbC are probably involved in the first and second methyl group transfer from TMA to HS-CoM. With respect to MMA utilization during growth on TMA, it became evident that mtmC4 had the highest transcript concentration of all mtmC genes followed by mtmC1 (Figure 5(a)). In detail, we observed a 130 and a 325-fold increase of mtmC1 and mtmC4 transcripts with TMA as substrate in comparison to methanol grown cells, respectively. The genes mtmC2 and mtmC3 showed a very low transcript abundance in TMA cells and a negligible increase of mRNA concentration compared to methanol grown cells (Figure 5(a)). Hence, we assume that mtmC1 and mtmC4 encoding corrinoid proteins and their corresponding MT1 enzymes (MtmB1 and MtmB4) are of major importance for the degradation of the intracellular intermediate MMA during growth on TMA. The genes mtbC and mtmC1 were also highly expressed when the cells were grown on DMA whereas the abundance of mtmC4 and mttC gene transcripts decreased (Figure 5(b)). When MMA was the substrate, only mtmC1 showed a high transcript concentration (Figure 5(c)). Interestingly during growth on methylamines, mtaC genes were expressed to almost the same extent as in cells grown on methanol (Figure 4). In summary, qRT-PCR analysis of key genes involved in methyl group transfer during methanogenesis led to the conclusion that M. luminyensis is able to adapt to TMA, DMA, and MMA as substrates, while the transcript levels of mtaC genes involved in methanol utilization were virtually unchanged. Hence, we assume that the organism prefers methanol as substrate and possesses a regulatory network for methylamine utilization.
3.4. Methane Formation in Resting Cells
Evidence in favor for the hypothesis that methanol is the preferred substrate came from experiments with resting cells. When resting cells obtained from methanol-grown cultures were incubated with methanol + H2 as substrate, CH4 was formed with a rate of 164 nmol min−1 mg protein−1 (Figure 6(a)). Interestingly, there was almost no methane production from TMA + H2, DMA + H2, or MMA + H2. A control experiment showed that the cells were not inactive but could produce methane in the same range of methanol-grown cells when methanol was added after 80 min (Figure 6(a)). This observation fits to the finding that transcripts of genes encoding corrinoid proteins for the degradation of methylamines were only found in very low amounts during growth on methanol (Table S) whereas transcripts of genes for methanol degradation were present in abundance. Similar experiments were performed with resting cells from TMA-grown cultures (Figure 6(b)). In this case, methane formation rates from TMA + H2 (150 nmol min−1 mg−1), DMA + H2 (153 nmol min−1 mg−1), or methanol + H2 (177 nmol min−1 mg−1) were in the same range compared to cells from methanol-grown cultures that converted methanol + H2. Only methanogenesis from MMA was a little slower with rates of 59 nmol min−1 mg−1. The experiments clearly showed that CH4 formation from methylamines was only possible when cultures were grown with TMA as substrate. These findings were in line with the results from qRT-PCR experiments which indicated that the genes involved in methylamine degradation were only transcribed to a sufficient extent during growth on TMA. Methanol + H2 was always consumed irrespective whether the cells were grown on methanol or TMA.
The order Methanomassiliicoccales is diverse, and members are found in habitats, which are highly relevant for global methane production. M. luminyensis was isolated from human feces and could evolve into a model organism of the order Methanomassiliicoccales; because the genome sequence is known, it is culturable in the laboratory and may have impacts on the human gut and on the biogas formation process . M. luminyensis showed the best growth rate with methanol + H2 as substrates. The final optical density strongly correlated with the methanol content, and the amount of methane increased proportionally. The highest final optical density was obtained with 110 mM methanol. Higher methanol concentrations did not lead to an increased final optical density. When methylamines were added in equimolar concentrations in reference to their methyl group content, similar final optical densities were obtained with 75 mM methanol, 75 mM MMA, 37.5 mM DMA, and 25 mM TMA as substrate, respectively. While the final optical densities of cultures growing on these substrates were in good agreement, the doubling times slightly varied from 1.8 d with methanol to 2.3 d with MMA.
A common method to compare methanogenic archaea with respect to the efficiency of their energy conserving systems is the determination of growth yields. The growth yield is defined as the amount of dry cell mass (g) which is obtained per mole of methane that is formed and is referred to as YCH4. YCH4 strongly correlates with the mode of energy conservation in methanogenic archaea. Hydrogenotrophic methanogens that do not possess cytochromes are only able to produce comparably low amounts of cell mass during methane formation, while archaea with cytochromes, for example, the genus Methanosarcina, produce higher cell mass under comparable conditions (Table 2). This observation argues for the hypothesis that the overall ATP gain is smaller in hydrogenotrophic methanogens with only 0.5 molecule of ATP compared to cytochrome containing methanogens which synthesize 1 molecule ATP per molecule methane [23, 24]. Here, the growth yield was determined for M. luminyensis on methanol + H2 and TMA + H2 which resembled the growth yield of hydrogenotrophic methanogens with 2.4 g of cell dry mass being formed per mole methane, respectively. This finding leads to the hypothesis that the ATP yield in M. luminyensis is comparable to the yield of hydrogenotrophic representatives with only 0.5 ATP molecules being formed during the generation of one molecule of methane. This is in good agreement with the metabolic model that was previously proposed for M. luminyensis [11, 12], where the translocation of 3-4 protons per two molecules of CH4 was predicted.
It was demonstrated that Methanosarcina species transfer methyl moieties from their substrates methanol or methylamines to HS-CoM forming methyl-coenzyme M (methyl-CoM) as central intermediate in methanogenesis . These reactions are catalyzed by the combined activities of methyltransferase 1 (MT1) [32, 33], a corrinoid protein and methyltransferase 2 (MT2) [34–36]. MT1 proteins are encoded by the genes mtaB and mttB, for methanol and TMA degradation, respectively (Figure 7) . Furthermore, mtbB and mtmB genes encode MT1 enzymes for the utilization of DMA and MMA [20, 38]. The enzymes transfer the methyl group from the substrates to the corresponding corrinoid proteins that are encoded by the genes mtaC for methanol, mttC for TMA, mtbC for DMA, and mtmC for MMA. Methyl moieties bound to the corrinoid proteins are transferred to HS-CoM by MT2 proteins (Figure 7) . Here, two classes are known which either use methylated MttC, MtbC, or MtmC proteins (MtbA) or MtaC as substrates (MtaA). However, it was found that MtaA is also involved in the transfer of the methyl group originating from TMA, albeit less efficiently [33, 39]. The final product from the methyl group transfer is methyl-CoM that is reduced to methane by the methyl-CoM reductase using coenzyme B (HS-CoB) as reductant.
The genome sequence of M. luminyensis indicated that several clusters comprise genes, which encode methyltransferases involved in methane formation from methanol and methylamines, respectively [5, 12]. For the demethylation of methanol, three copies of genes for MT1 (mtaB1, 2, and 3), the corrinoid protein (mtaC1, 2, and 3), and one gene encoding the methanol-specific MT2 (mtaA) were identified (Figure 7). The gene clusters for methylamine utilization are even more complex. The largest cluster was found on contig 23 of the genome, which contained a full set of genes involved in DMA (mtbBC) and TMA (mttBC) degradation, including genes encoding permeases for TMA (mttP) and DMA (mtbP) uptake. Furthermore, genes encoding enzymes for the synthesis of pyrrolysine (pylBCD) and tRNAPyl (pylS) were identified (not shown) . While mtbBC and mttBC were found in single copies, four clusters for MMA utilization (mtmBC) were detected. One cluster on contig 23 was located next to the mtt/mtb/pyl locus but was encoded on the complementary DNA strand (Figure 7). Two copies were found on contig 4, which were separated by a second pylBCD/pylS cluster. The fourth mtmBC gene cluster on contig 23 was connected to a third pylC gene and a gene encoding the nitrogen regulator PII (not shown) .
Interestingly, all genes encoding MT1 enzyme for methylamine degradation contain the amber codon UAG. Hence, all methylamine corrinoid methyltransferases (MttB, MtbB, and MtmB) possess the 22nd proteogenic amino acid pyrrolysine . It is synthesized by PylBCD from two lysine molecules and bound to a Pyl-specific tRNA by the tRNA synthetase PylS for incorporation via the amber codon (UAG) . Such a system has been found only in the methanogens of the family Methanosarcinaceae and in a small number of bacteria.
From our results, it became evident that M. luminyensis adapts to different methanogenic substrates. qRT-PCR analysis revealed differences in mRNA abundances of genes encoding the enzymes for the utilization of methanol and methylamines, respectively. An interesting aspect was the fact that only one (mtaC2) out of the three mtaC genes was highly expressed. Similar results were obtained for Methanosarcina species where qRT-PCR, proteome analyses, and reporter gene fusion assays, as well as deletion mutant studies, were performed to investigate the role of the different methyltransferase systems in the degradation of methanol [37, 40–43]. It is tempting to speculate that mtaC2 in M. luminyensis forms an operon structure with mtaB2. Evidence for this presumption was found in Ms. barkeri and Ms. mazei where mtaBC genes are cotranscribed [17, 22]. Therefore, it can be concluded that in M. luminyensis methyl group, transfer from methanol to the corrinoid protein MtaC2 is catalyzed by MtaB2. The methyl group of CH3-MtaC2 is then transferred to coenzyme M by the catalytic activity of the MT2 methyltransferase MtaA. Furthermore, qRT-PCR experiments showed increased mRNA levels of the mttC and mtbC genes in TMA-grown cultures reaching ratios up to 300-fold of those in methanol-grown cells. The genes mttC and mtbC are part of a large gene cluster containing the corresponding mttB and mtbB genes as well as genes encoding potential permeases for TMA and DMA uptake, respectively (Figure 7). Hence, all results point to the presence of a highly elaborate mechanism of gene regulation for optimal TMA utilization in M. luminyensis. In addition, it became evident that the mtaC genes were not differentially expressed and especially mtaC2 revealed high expression levels during growth on methanol and all methylamines, respectively. These findings were also underlined by experiments with resting cells. Cells, which were grown on methanol, could produce CH4 from methanol + H2 but not from methylamines + H2 suggesting that genes involved in methylamine degradation are stringently repressed during growth on methanol. In contrast, resting cells could use methylamines as substrates when they were adapted to and grown on TMA. However, in this case, methanol still yielded the highest methane production rate, which argues for the hypothesis that genes for methanol degradation are constitutively expressed and highly transcribed independently from the substrate.
Information about growth parameters of M. luminyensis and other human-associated methanogens are scarce, although M. luminyensis could evolve into a suitable model organism for studying the biochemistry of methanogenic archaea from the order Methanomassiliicoccales and the biology of human-associated archaea in general. Furthermore, for a successful development of curative treatments (“Archaebiotics”) using M. luminyensis, it is essential to analyze the growth behavior for the development of methods that permit efficient growth and allow the production of sufficient cell mass. In recent studies, only low cell yields were obtained with M. luminyensis . Here, we present comprehensive data about how growth of this organism can be improved by using different substrates and by increasing the substrate concentration. Moreover, this work provides insights into the first steps of substrate utilization where the methyl groups from methanol or methylamines are transferred to HS-CoM by substrate-specific methyltransferases via certain corrinoid proteins. It became clear from qRT-PCR analysis and experiments using resting cells that methanol is the preferred substrate of this organism. This leads to the question whether the constitutive expression of mta genes reflects the greater availability of methanol in comparison to TMA in the human gut as natural habitat of M. luminyensis. Interestingly, it became evident from the analysis of volatile fatty acids in human feces that methanol is indeed more abundant in the intestinal tract than methylamines while elevated TMA levels are only associated with certain diseases .
|CoM-S-S-CoB:||Disulfide from HS-CoM and HS-CoB|
|HS-CoB:||7-Mercaptoheptanoyl threonine phosphate|
|MT2, substrate:||5-Hydroxybenzimidazolylcobamide methyltransferase|
|YCH4:||Growth yield per mole of methane.|
Conflicts of Interest
The authors declare that they have no competing interests.
The authors thank Dr. Corinna Bang and Professor Dr. Ruth Schmitz-Streit from the University of Kiel for the helpful discussions concerning the cultivation of M. luminyensis. The authors also thank Dr. Sarah Refai for the critical reading of the manuscript. This work was supported by Deutsche Forschungsgemeinschaft (DE488/12-1).
Supplementary Figure 1: Dependence of methanol concentration and final optical density. Supplemntary 2: Dependence on acetate consumption and dry weight formation in the exponential growth phase of M. luminyensis.
- J. G. Ferry, “Fundamentals of methanogenic pathways that are key to the biomethanation of complex biomass,” Current Opinion in Biotechnology, vol. 22, no. 3, pp. 351–357, 2011.
- N. Gaci, G. Borrel, W. Tottey, P. W. O’Toole, and J. F. Brugère, “Archaea and the human gut: new beginning of an old story,” World Journal of Gastroenterology, vol. 20, no. 43, pp. 16062–16078, 2014.
- B. Dridi, M. L. Fardeau, B. Ollivier, D. Raoult, and M. Drancourt, “Methanomassiliicoccus luminyensis gen. nov., sp. nov., a methanogenic archaeon isolated from human faeces,” International Journal of Systematic and Evolutionary Microbiology, vol. 62, Part 8, pp. 1902–1907, 2012.
- K. Paul, J. O. Nonoh, L. Mikulski, and A. Brune, ““Methanoplasmatales,” Thermoplasmatales-related archaea in termite guts and other environments, are the seventh order of methanogens,” Applied and Environmental Microbiology, vol. 78, no. 23, pp. 8245–8253, 2012.
- G. Borrel, N. Parisot, H. M. Harris et al., “Comparative genomics highlights the unique biology of Methanomassiliicoccales, a Thermoplasmatales-related seventh order of methanogenic archaea that encodes pyrrolysine,” BMC Genomics, vol. 15, no. 1, pp. 679–701, 2014.
- T. Iino, H. Tamaki, S. Tamazawa et al., “Candidatus Methanogranum caenicola: a novel methanogen from the anaerobic digested sludge, and proposal of Methanomassiliicoccaceae fam. nov. and Methanomassiliicoccales ord. nov., for a methanogenic lineage of the class Thermoplasmata,” Microbes and Environments, vol. 28, no. 2, pp. 244–250, 2013.
- G. Borrel, P. W. O’Toole, H. M. Harris, P. Peyret, J. F. Brugère, and S. Gribaldo, “Phylogenomic data support a seventh order of methylotrophic methanogens and provide insights into the evolution of methanogenesis,” Genome Biology and Evolution, vol. 5, no. 10, pp. 1769–1780, 2013.
- U. Deppenmeier, “The unique biochemistry of methanogenesis,” Progress in Nucleic Acid Research and Molecular Biology, vol. 71, pp. 223–283, 2002.
- T. L. Miller and M. J. Wolin, “Methanosphaera stadtmaniae gen. nov., sp. nov.: a species that forms methane by reducing methanol with hydrogen,” Archives of Microbiology, vol. 141, no. 2, pp. 116–122, 1985.
- W. F. Fricke, H. Seedorf, A. Henne et al., “The genome sequence of Methanosphaera stadtmanae reveals why this human intestinal archaeon is restricted to methanol and H2 for methane formation and ATP synthesis,” Journal of Bacteriology, vol. 188, no. 2, pp. 642–658, 2006.
- L. Kröninger, S. Berger, C. Welte, and U. Deppenmeier, “Evidence for the involvement of two different heterodisulfide reductases in the energy conserving system of Methanomassiliicoccus luminyensis,” FEBS Journal, vol. 283, no. 3, pp. 472–483, 2016.
- K. Lang, J. Schuldes, A. Klingl, A. Poehlein, R. Daniel, and A. Brune, “New mode of energy metabolism in the seventh order of methanogens as revealed by comparative genome analysis of “Candidatus Methanoplasma termitum”,” Applied and Environmental Microbiology, vol. 81, no. 4, pp. 1338–1352, 2015.
- G. Borrel, N. Gaci, P. Peyret, P. W. O’Toole, S. Gribaldo, and J. F. Brugère, “Unique characteristics of the pyrrolysine system in the 7th order of methanogens: implications for the evolution of a genetic code expansion cassette,” Archaea, vol. 2014, Article ID 374146, 11 pages, 2014.
- J. F. Brugère, G. Borrel, N. Gaci, W. Tottey, P. W. O’Toole, and C. Malpuech-Brugère, “Archaebiotics: proposed therapeutic use of archaea to prevent trimethylaminuria and cardiovascular disease,” Gut Microbes, vol. 5, no. 1, pp. 5–10, 2014.
- R. J. Mackay, C. J. McEntyre, C. Henderson, M. Lever, and P. M. George, “Trimethylaminuria: causes and diagnosis of a socially distressing condition,” The Clinical Biochemist Review, vol. 32, no. 1, pp. 33-34, 2011.
- H. Hippe, D. Caspari, K. Fiebig, and G. Gottschalk, “Utilization of trimethylamine and other N-methyl compounds for growth and methane formation by Methanosarcina barkeri,” Proceedings of the National Academy of Sciences of the United States of America, vol. 76, no. 1, pp. 494–498, 1979.
- C. Krätzer, P. Carini, R. Hovey, and U. Deppenmeier, “Transcriptional profiling of methyltransferase genes during growth of Methanosarcina mazei on trimethylamine,” Journal of Bacteriology, vol. 191, no. 16, pp. 5108–5115, 2009.
- M. A. Larkin, G. Blackshields, N. P. Brown et al., “Clustal W and Clustal X version 2.0,” Bioinformatics, vol. 23, no. 21, pp. 2947-2948, 2007.
- J. P. Folsom and R. P. Carlson, “Physiological, biomass elemental composition and proteomic analyses of Escherichia coli ammonium limited chemostat growth, and comparison with iron- and glucose-limited chemostat growth,” Microbiology, vol. 161, no. 8, pp. 1659–1670, 2015.
- L. Paul, D. J. Ferguson, and J. A. Krzycki, “The trimethylamine methyltransferase gene and multiple dimethylamine methyltransferase genes of Methanosarcina barkeri contain in-frame and read-through amber codons,” Journal of Bacteriology, vol. 182, no. 9, pp. 2520–2529, 2000.
- J. A. Krzycki, “The path of lysine to pyrrolysine,” Current Opinion in Chemical Biology, vol. 17, no. 4, pp. 619–625, 2013.
- K. Sauer, U. Harms, and R. K. Thauer, “Methanol: coenzyme M methyltransferase from Methanosarcina barkeri. Purification, properties and encoding genes of the corrinoid protein MT1,” European Journal of Biochemistry, vol. 243, no. 3, pp. 670–677, 1997.
- R. K. Thauer, A. K. Kaster, H. Seedorf, W. Buckel, and R. Hedderich, “Methanogenic archaea: ecologically relevant differences in energy conservation,” Nature Reviews Microbiology, vol. 6, no. 8, pp. 579–591, 2008.
- A. K. Kaster, J. Moll, K. Parey, and R. K. Thauer, “Coupling of ferredoxin and heterodisulfide reduction via electron bifurcation in hydrogenotrophic methanogenic archaea,” Proceedings of the National Academy of Sciences of the United States of America, vol. 108, no. 7, pp. 2981–2986, 2011.
- A. J. B. Zehnder and K. Wuhrmann, “Physiology of Methanobacterium strain AZ,” Archives of Microbiology, vol. 111, no. 3, pp. 199–205, 1977.
- A. M. Roberton and R. S. Wolfe, “Adenosine triphosphate pools in Methanobacterium,” Journal of Bacteriology, vol. 102, no. 1, pp. 43–51, 1970.
- J. A. Robinson and J. M. Tiedje, “Competition between sulfate-reducing and methanogenic bacteria for H2 under resting and growing conditions,” Archives of Microbiology, vol. 137, no. 1, pp. 26–32, 1984.
- P. J. Weimer and J. G. Zeikus, “One carbon metabolism in methanogenic bacteria,” Archives of Microbiology, vol. 119, no. 1, pp. 49–57, 1978.
- M. R. Smith and R. A. Mah, “Acetate as sole carbon and energy source for growth of Methanosarcina strain 227,” Applied and Environmental Microbiology, vol. 39, no. 5, pp. 993–999, 1980.
- M. R. Smith and R. A. Mah, “Growth and methanogenesis by Methanosarcina strain 227 on acetate and methanol,” Applied and Environmental Microbiology, vol. 36, no. 6, pp. 870–879, 1978.
- M. Rother and J. A. Krzycki, “Selenocysteine, pyrrolysine, and the unique energy metabolism of methanogenic archaea,” Archaea, vol. 2010, Article ID 453642, 14 pages, 2010.
- U. Harms and R. K. Thauer, “Methylcobalamin:coenzyme M methyltransferase isoenzymes MtaA and MtbA from Methanosarcina barkeri. Cloning, sequencing and differential transcription of the encoding genes, and functional overexpression of the mtaA gene in Escherichia coli,” European Journal of Biochemistry, vol. 235, no. 3, pp. 653–659, 1996.
- D. J. Ferguson Jr, J. A. Krzycki, and D. A. Grahame, “Specific roles of methylcobamide:coenzyme M methyltransferase isozymes in metabolism of methanol and methylamines in Methanosarcina barkeri,” Journal of Biological Chemistry, vol. 271, no. 9, pp. 5189–5194, 1996.
- D. J. Ferguson Jr and J. A. Krzycki, “Reconstitution of trimethylamine-dependent coenzyme M methylation with the trimethylamine corrinoid protein and the isozymes of methyltransferase II from Methanosarcina barkeri,” Journal of Bacteriology, vol. 179, no. 3, pp. 846–852, 1997.
- S. A. Burke and J. A. Krzycki, “Reconstitution of monomethylamine:coenzyme M methyl transfer with a corrinoid protein and two methyltransferases purified from Methanosarcina barkeri,” Journal of Biological Chemistry, vol. 272, no. 26, pp. 16570–16577, 1997.
- D. J. Ferguson Jr, N. Gorlatova, D. A. Grahame, and J. A. Krzycki, “Reconstitution of dimethylamine:coenzyme M methyl transfer with a discrete corrinoid protein and two methyltransferases purified from Methanosarcina barkeri,” Journal of Biological Chemistry, vol. 275, no. 37, pp. 29053–29060, 2000.
- M. A. Pritchett and W. W. Metcalf, “Genetic, physiological and biochemical characterization of multiple methanol methyltransferase isozymes in Methanosarcina acetivorans C2A,” Molecular Microbiology, vol. 56, no. 5, pp. 1183–1194, 2005.
- S. A. Burke, S. L. Lo, and J. A. Krzycki, “Clustered genes encoding the methyltransferases of methanogenesis from monomethylamine,” Journal of Bacteriology, vol. 180, no. 13, pp. 3432–3440, 1998.
- A. Bose, M. A. Pritchett, and W. W. Metcalf, “Genetic analysis of the methanol- and methylamine-specific methyltransferase 2 genes of Methanosarcina acetivorans C2A,” Journal of Bacteriology, vol. 190, no. 11, pp. 4017–4026, 2008.
- A. Bose, M. A. Pritchett, M. Rother, and W. W. Metcalf, “Differential regulation of the three methanol methyltransferase isozymes in Methanosarcina acetivorans C2A,” Journal of Bacteriology, vol. 188, no. 20, pp. 7274–7283, 2006.
- Y. H. Ding, S. P. Zhang, J. F. Tomb, and J. G. Ferry, “Genomic and proteomic analyses reveal multiple homologs of genes encoding enzymes of the methanol:coenzyme M methyltransferase system that are differentially expressed in methanol- and acetate-grown Methanosarcina thermophila,” FEMS Micrbiology Letters, vol. 215, no. 1, pp. 127–132, 2002.
- L. Li, Q. Li, L. Rohlin et al., “Quantitative proteomic and microarray analysis of the archaeon Methanosarcina acetivorans grown with acetate versus methanol,” Journal of Proteome Research, vol. 6, no. 2, pp. 759–771, 2007.
- A. Bose and W. W. Metcalf, “Distinct regulators control the expression of methanol methyltransferase isozymes in Methanosarcina acetivorans C2A,” Molecular Microbiology, vol. 67, no. 3, pp. 649–661, 2008.
- C. E. Garner, S. Smith, B. de Lacy Costello et al., “Volatile organic compounds from feces and their potential for diagnosis of gastrointestinal disease,” FASEB Journal, vol. 21, no. 8, pp. 1675–1688, 2007.
Copyright © 2017 Lena Kröninger et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.