Abstract
Background
Forestomach fermentation in Australian marsupials such as wallabies and kangaroos, though analogous to rumen fermentation, results in lower methane emissions. Insights into hydrogenotrophy in these systems could help in devising strategies to reduce ruminal methanogenesis. Reductive acetogenesis may be a significant hydrogen sink in these systems and previous molecular analyses have revealed a novel diversity of putative acetogens in the tammar wallaby forestomach.
Results
Methanogen-inhibited enrichment cultures prepared from tammar wallaby forestomach contents consumed hydrogen and produced primarily acetate. Functional gene (formyltetrahydrofolate synthetase and acetyl-CoA synthase) analyses revealed a restricted diversity of Clostridiales species as the putative acetogens in the cultures. A new acetogen (growth on H2/CO2 with acetate as primary end product) designated isolate TWA4, was obtained from the cultures. Isolate TWA4 classified within the Lachnospiraceae and demonstrated >97% rrs identity to previously isolated kangaroo acetogens. Isolate TWA4 was a potent hydrogenotroph and demonstrated excellent mixotrophic growth (concomitant consumption of hydrogen during heterotrophic growth) with glycerol. Mixotrophic growth of isolate TWA4 on glycerol resulted in increased cell densities and acetate production compared to autotrophic growth. Co-cultures with an autotrophic methanogen Methanobrevibacter smithii revealed that isolate TWA4 performed reductive acetogenesis under high hydrogen concentration (>5 mM), but not at low concentrations. Under heterotrophic growth conditions, isolate TWA4 did not significantly stimulate methanogenesis in a co-culture with M. smithii contrary to the expectation for organisms growing fermentatively.
Conclusions
The unique properties of tammar wallaby acetogens might be contributing factors to reduced methanogen numbers and methane emissions from tammar wallaby forestomach fermentation, compared to ruminal fermentation. The macropod forestomach may be a useful source of acetogens for future strategies to reduce methane emissions from ruminants, particularly if these strategies also include some level of methane suppression and/or acetogen stimulation, for example by harnessing mixotrophic growth capabilities
Electronic supplementary material
The online version of this article (doi:10.1186/s12866-014-0314-3) contains supplementary material, which is available to authorized users.
Keywords: Acetogen, Acetogenesis, Tammar wallaby, Rumen, Methanogenesis
Background
Methane is a potent greenhouse gas that has been implicated in global warming [1]. Enteric fermentation of ruminant livestock is the largest source of anthropogenic methane, contributing between 20 and 25% of global methane emissions [2]. During ruminal fermentation, methanogenic archaea use hydrogen to reduce carbon dioxide or methylated compounds to methane, contributing to global methane emissions and representing a loss of between 2 and 12% ingested feed energy for the ruminant [3]. Australian macropod marsupials such as kangaroos and wallabies exhibit foregut fermentation analogous to ruminants but resulting in lower methane emissions [4-6], which suggests either lower hydrogen production from foregut fermentation or the functioning of alternative hydrogen disposal mechanisms to methanogenesis in these animals. If the latter, understanding hydrogenotrophy in these foregut systems may provide insight into mechanisms for redirecting hydrogen away from methanogenesis in ruminants. Acetogenesis (4H2 + 2CO2 → CH3COOH +2H2O) may represent a significant hydrogen sink in the foregut of native Australian marsupials and these animals may be a source of novel acetogens [7-10]. Recent molecular analyses revealed a diverse and novel population of putative acetogens in the forestomach of the tammar wallaby that was significantly different to the population present in ruminants [8]. Potentially, acetogen population differences between native Australian marsupials and ruminants is causal or results from reduced methane emissions from foregut fermentation in these animals. The aims of the present study were to investigate the novel acetogen diversity from the tammar wallaby forestomach using enrichment cultures and molecular analysis of enrichment cultures, as well as to isolate acetogens from the tammar wallaby forestomach and investigate factors that may stimulate their hydrogenotrophic capacities. We report here the isolation of a novel acetogen, isolate TWA4 from the tammar wallaby forestomach and its hydrogenotrophic capacity, mixotrophic growth capabilities and interactions with a methanogen in co-culture under autotrophic and heterotrophic growth conditions. We also report on partial genomic information from isolate TWA4 relating to the Wood-Ljungdahl pathway genes and to genes for glycerol metabolism.
Results
Characterisation of tammar wallaby forestomach acetogen enrichment cultures Hydrogen consumption and acetate production
Acetogen enrichment cultures from tammar wallaby forestomach contents consumed net hydrogen and carbon dioxide. Acetic acid was the major end product detected, a small amount of sulphide and minor amounts of other acids were also produced and no methane was detected (Additional file 1). Acetate production accounted for 61 ± 2.3% of hydrogen consumed based on stoichiometry of the acetyl-CoA pathway (H2 consumption:acetate production ratio for enrichment cultures was 6.58 ± 0.256).
Molecular analysis of tammar wallaby forestomach acetogen enrichment cultures
The 16S rRNA gene (rrs) library (n = 96) from tammar wallaby forestomach acetogen enrichment cultures revealed a restricted bacterial diversity (9 OTUs) and rarefaction analysis indicated that an acceptable level of sequencing coverage had been achieved (Additional file 2). One OTU from the cultures showed > 97% rrs identity to Enterococcus faecium, another contained sequences that demonstrated > 97% rrs identity to recently isolated kangaroo acetogens YE273, YE266 and YE257 that are yet to be formally classified [10] and the remaining OTUs were classified as Clostridiales or Tenericutes sequences and did not demonstrate > 97% sequence identity to any named species. The rrs from an isolate later obtained from the cultures (isolate TWA4) clustered within the OTU demonstrating > 97% identity to kangaroo acetogens (Additional file 3).
FTHFS sequences (n = 64) from tammar wallaby forestomach enrichments clustered into four OTUs that affiliated with the Clostridiaceae and demonstrated homoacetogen similarity (HS) scores > 90% (Additional file 4a). Rarefaction analysis indicated that an acceptable level of coverage had been achieved for FTHFS sequences (Additional file 4b). Sequences in one FTHFS OTU (OTU 2, Additional file 4a) were the same as a sequence detected in the tammar wallaby previously [8]. The two largest FTHFS OTUs from the enrichments grouped with two copies of FTHFS recovered from isolate TWA4, which was later isolated from the cultures (Additional file 4a). ACS sequences (n = 41) from the enrichment cultures also clustered into four OTUs, one identical to an ACS from Blautia hydrogenotrophica and detected in the tammar wallaby previously [8], the others affiliating with the Lachnospiraceae or forming a sister group to the Clostridiaceae. Sequences in the two largest ACS OTUs from the enrichments were identical to two ACS sequences recovered from isolate TWA4, later isolated from these enrichments (Additional file 5a); one of these sequences had been reported in the tammar wallaby previously [8]. Rarefaction analysis indicated that an acceptable level of coverage had been achieved for ACS sequences (Additional file 5b).
Isolation and preliminary characterisation of acetogens from the tammar wallaby forestomach
Three isolates in pure culture that were obtained from tammar wallaby forestomach enrichment cultures were considered potential acetogens after demonstrating the presence of fhs and showing net H2 and CO2 consumption and producing acetate as the major end product when grown on modified AC11.1 medium with H2:CO2 provided. Detailed analyses were only performed on one isolate, hereafter referred to as isolate TWA4. Isolate TWA4 was a strict anaerobe. Phylogenetically, isolate TWA4 classified within Cluster XIV of the Clostridium sub-phylum, within the family Lachnospiraceae and demonstrated > 97% rrs identity to three recently isolated kangaroo acetogens: strains YE273, YE266 and YE257 (Additional file 3). The nearest named isolate to these species was Ruminococcus gnavus, which demonstrated only 92.35% rrs identity to isolate TWA4. The nearest named rumen acetogen was Acetitomaculum ruminis which demonstrated 88.52% identity to isolate TWA4 (Additional file 3). Two copies of each of the key reductive acetogenesis genes acsB and fhs were recovered from isolate TWA4. The FTHFS sequences showed ~93.9% amino acid similarity to each other and both affiliated with the Clostridiaceae (sequences TWA4_1 and TWA4_2, Additional file 4a). The ACS sequences demonstrated only 63.38% amino acid identity to each other and one copy affiliated with the Clostridiaceae while the second copy of acsB affiliated distantly with the Lachnospiraceae (sequences TWA4_1 and TWA4_2, Additional file 5a).
Morphology and cell structure of tammar wallaby isolate TWA4
Isolate TWA4 grew as straight rods, varying in length from 1.0 to 2.8 μm and diameter from 0.7 to 2.0 μm (Figure 1a). Cells mainly occurred in pairs or sometimes in clusters or short chains of three to five cells. Electron microscopy revealed a typical Gram positive cell wall structure for TWA4 (Figure 1b), while staining properties and cellular morphology varied with culture conditions. For example, when glycerol was included in the culture medium, TWA4 cells displayed white, electron-luscent dense areas (Figure 1a), that were not present in cells grown on medium without glycerol (Figure 1b). Also, compared to TWA4 cells grown without glycerol, cells grown with glycerol displayed a smaller amount of capsular material and were more prone to forming short chains. Short stacks of membranes were frequently seen in cells grown without glycerol (Figure 1b) but never when glycerol was present in the medium.
Metabolic and mixotrophic capabilities of tammar wallaby isolate TWA4
When grown on modified AC11.1 medium, isolate TWA4 consumed net hydrogen (3206 ± 156 μmoles) and carbon dioxide (1745 ± 58 μmoles) with acetate (523 ± 141 μmoles) as the major end product (Figure 2a). The maximal cell density under these conditions as measured by OD600 was ~0.2 (Figure 2a). There was large variability in the hydrogen consumption:acetate production ratios of individual cultures in this experiment, possibly as a result of subsampling gases and short chain fatty acids (SCFAs) every 6 hours throughout the culture progression. When cultures of isolate TWA4 were not disturbed during incubation and gases and SCFAs were measured only at end point, hydrogen consumption:acetate production ratios of 5.56 ± 0.263 were observed.
Glycerol was found to be stimulatory to the growth and acetate production of isolate TWA4 with hydrogen consumed concomitantly, indicating mixotrophy. Over a 48 hour period, isolate TWA4 produced significantly more acetate and higher cell densities when grown on medium with glycerol alone (p < 0.05) or with glycerol plus H2:CO2 (p < 0.001), than when grown on medium with only H2:CO2 available as substrate (Figure 2). Hydrogen was consumed by isolate TWA4 during growth under all three conditions and hydrogen consumption was not significantly different between medium with only H2:CO2 available as substrates and medium with both glycerol and H2:CO2 provided (p > 0.05, see Figure 2a and c). Hydrogen did not accumulate in significant amounts during growth of TWA4 on glycerol alone and the residual hydrogen present in the headspace of culture from medium preparation in an anaerobic chamber, was consumed (Figure 2b). During growth on glycerol alone, glycerol was consumed within 48 hours, acetate was the major end product (glycerol consumption to acetate production ratios were ~ 0.81), minor amounts of formate and citrate were also produced (Figure 3a) and 1,3-propanediol and other alcohols were not detected. During growth on glycerol alone, hydrogen accumulated to a maximum of 3.46 ± 0.11 μmoles (in a 17 ml headspace, ~4620 ppm hydrogen) within 24 hours and thereafter declined to 1.35 ± 0.29 μmoles over the next 24 hours (Figure 3b).
Co-culture of isolate TWA4 with a methanogen
Cultures of M. smithii and isolate TWA4 when grown together under H2:CO2 consumed net hydrogen to produce both acetate and methane as end products, indicating successful growth of both strains. During the first 18 hours of growth, the pattern of hydrogen consumption and acetate production in co-cultures followed that observed for isolate TWA4 alone (Figure 4a, c), while methane production was significantly (p <0.01) reduced across this period for co-cultures compared to cultures of M. smithii alone (Figure 4b). However, by 18 hours the hydrogen concentration in the headspace of culture tubes declined to approximately 82 μmoles (in a 17 ml headspace, ~4.8 mM), no further acetate production was observed and the remaining hydrogen was consumed and methanogenesis started to dominate acetogenesis (Figure 4a-c).
In co-cultures of isolate TWA4 and M. smithii without H2:CO2 provided but with glycerol as a substrate (Figure 4d-f), acetate production was not significantly different to that observed by isolate TWA4 alone (p > 0.05) and the minimal methane that was produced was not significantly different (p = 0.08) to that observed in pure cultures of M. smithii without an overpressure of H2:CO2 in the headspace (i.e. with only the residual hydrogen from the anaerobic chamber atmosphere in culture headspaces).
Genomic analysis of isolate TWA4 with respect to the acetyl-CoA pathway and potential glycerol metabolism pathways
Sequence reads assembled using Newbler (v 2.6) generated eight scaffolds with an estimated genome size of 3.4 Mb at 12 times coverage. 98.69% of the reads and 85.36% of the contigs were assembled into the largest scaffold of just over 3.1 Mb. The average gap in the assembled data was calculated as 870 bp. Orphan contigs greater than 500 bp and scaffolds produced 3.2 Mb of data that was comprised of 3038 open reading frames of which 34% were of unknown function.
Genes encoding the enzymes of the complete acetyl-CoA pathway were present in the genome of isolate TWA4 (Figure 5) and key genes of this pathway clustered together (Figure 6) with a gene order that did not resemble any of the five groups of Wood-Ljungdahl pathway gene clusters reported to date [11]. Genes encoding enzymes for the degradation of glycerol to acetate via glycerol-3-phosphate were found in the genome of isolate TWA4 (see Figure 7) and genes encoding the enzymes glycerol dehydrogenase (EC 1.1.1.6) and dihydroxyacetone kinase (EC 2.7.1.29) which are responsible for conversion of glycerol to dihydroxyacetone-phosphate via dihydroxyacetone, were not evident in the genome of isolate TWA4 [e.g. for an overview of glycerol degradation pathways see [12]].
Discussion
In order to fully understand complex microbial ecosystems and/or harness microbial activities for any useful purpose, it is essential that researchers combine the strengths of both cultivation and molecular-based techniques. In the present study we employed a combination of cultivation and molecular approaches to successfully enrich for acetogens from tammar wallaby forestomach contents, which had previously only been investigated by molecular methods [8]. Molecular analysis of enrichment cultures in the present study revealed novel putative acetogens with functional genes affiliating between the Lachnospiraceae and Clostridiaceae and not close to sequences from any previously known acetogen (Additional files 4a and 5a). We successfully isolated one of these novel acetogens (isolate TWA4) which classified within the Lachnospiraceae and may belong to the same species as recently isolated acetogens from the forestomach of eastern grey (Macropus giganteus) and red kangaroos (Macropus rufus) [10].
Isolate TWA4 was a potent hydrogenotroph rapidly consuming exogenous hydrogen and carbon dioxide with acetate as the sole or primary end product. Hydrogen consumption:acetate ratios for isolate TWA4 were at times higher than expected based on stoichiometry of the acetyl-CoA pathway of reductive acetogenesis (4H2 + 2CO2 → CH3COOH +2H2O), most likely due to consumption of hydrogen and carbon dioxide for formation of cell carbon and capsular material for new biomass, as end products other than acetate were not detected. Genomic analysis confirmed the presence of all genes for the Wood-Ljungdahl acetyl-CoA pathway of reductive acetogenesis in isolate TWA4 (Figure 5). However, the order of key genes of this pathway in the isolate TWA4 genome was not consistent with any of the previously reported gene orders for other microorganisms possessing this pathway [11]. The order of key Wood-Ljungdahl pathway genes in TWA4 was remarkably similar to that of two other species whose genome has recently been completed, Blautia hydrogenotrophica and Ruminococcus obeum (Figure 6) and we propose that this ordering constitutes a new gene order group. Though this gene ordering is most similar to the gene order of what is currently known as group C [11], isolate TWA4, B. hydrogenotrophica and R. obeum all show replacement of the formyl tetrahydrofolate synthase, the bifunctional formyltetrahydrofolate cyclohydrolase/dehydrogenase and methylene tetrahydrofolate reductase cluster of group C with a second acsB copy (Figure 6). Multiple copies of fhs and acsB have been detected in other pure culture acetogens using PCR-based methods previously [8]. The presence of two acsB and fhs in isolate TWA4, which match to the majority of acsB and fhs sequences recovered from tammar wallaby acetogen enrichment cultures (Additional files 4a and 5a), indicate that isolate TWA4 was the dominant acetogen enriched for in the culture approach used in this study. Functional genes from strain TWA4 have been recovered from the tammar wallaby forestomach previously [8] indicating that this species forms a substantial proportion of the acetogen population in the tammar wallaby forestomach naturally and is detectable without any selection or cultivation bias. However, these functional genes were not dominant within FTHFS and ACS libraries from the tammar wallaby forestomach naturally [8] suggesting that other, potentially major, acetogens are present in vivo and were not selected for with the cultivation conditions used in the present study.
In addition to autotrophic growth, isolate TWA4 demonstrated excellent mixotrophic capabilities, consuming hydrogen just as rapidly during growth on glycerol and H2:CO2 as on H2:CO2 alone and producing significantly more acetate and more than twice the cell mass as a result of mixotrophy. Mixotrophy influences the competitiveness of acetogens over methanogens in some ecosystems [13] and has been suggested as an important trait required for any acetogen that will be used in strategies for reducing ruminal methanogenesis [14,15]. While many acetogens are capable of mixotrophic growth, to date only one rumen acetogen with this ability has been reported [14]. It is generally thought that most rumen acetogens growing in the presence of carbohydrates will ferment the available substrate rather than grow autotrophically or mixotrophically (e.g. as for strain ser8 in [14]) and in a mixed community they would therefore make hydrogen available for interspecies transfer [16] to methanogens. Our investigations of isolate TWA4 in pure culture and in co-culture with a methanogen do not support this idea. In contrast to typical fermentative growth on glycerol (e.g. for Thermotoga spp.) which results in accumulation of acetate, CO2 and H2 [17] isolate TWA4 did not accumulate hydrogen as an end product. Rather, hydrogen generated during fermentation was consumed (Figure 3b), suggesting that isolate TWA4 was able to internally shuttle or utilise most of the reducing equivalents generated during fermentation. Furthermore, when isolate TWA4 was grown heterotrophically with glycerol as a substrate, in co-culture with a methanogen, methanogenesis was not significantly stimulated (p =0.08). Further experiments are necessary to confirm this finding with other methanogens and over longer growth periods, however it seems possible from these data that there may be potential to find appropriate acetogens to serve as alternative hydrogenotrophs in the rumen ecosystem in the future.
Although isolate TWA4 successfully performed reductive acetogenesis in the presence a hydrogenotrophic methanogen when hydrogen was available at high concentrations (Figure 4), isolate TWA4 was not able to compete with a methanogen for hydrogen when hydrogen concentrations in the headspace were low (in this case < 5 mM, Figure 4), as expected based on the energetics of reductive acetogenesis and methanogenesis [18,19]. These findings are in agreement with the available literature which indicates that autotrophic acetogenesis alone will not dominate over methanogens under natural rumen conditions (e.g. see [18]). However, potentially acetogen stimulation (e.g. by harnessing mixotrophic capabilities) along with methanogen suppression could be a useful strategy to establishing reductive acetogenesis as an alternative hydrogen sink in the rumen.
Conclusions
Acetogens previously identified from the tammar wallaby forestomach by molecular methods were successfully enriched in culture. An acetogen obtained from these cultures, isolate TWA4, was a potent hydrogenotroph and capable of mixotrophic growth with glycerol. Under heterotrophic conditions with glycerol, isolate TWA4 did not significantly stimulate methane production by a co-cultured methanogen, suggesting that isolate TWA4 might be able to internally recycle some of the reducing equivalents it generates during fermentation. While more detailed experiments with other methanogens and growth conditions are necessary to support our findings, the unique properties of tammar wallaby acetogens that we have observed could potentially be contributing factors to reduced methanogenesis and methanogen numbers in the tammar wallaby forestomach compared to the rumen. The macropod forestomach may be a useful source of acetogens for future strategies to reduce methane emissions from ruminants if these strategies also include some level of methane suppression and/or acetogen stimulation for example by harnessing mixotrophic growth capabilities (e.g. [15,20-23]).
Methods
Sample collection
Forestomach contents were collected from three euthanized female tammar wallabies from a captive colony that had been grazing pasture and receiving a commercial grain pellet mix supplement, as reported previously [24,25]. The animals were sampled in November 2006 and at the time had free range access to pastures composed predominantly of Timothy Canary grass (Phalaris angusta) and were also provided with a commercial pellet mix containing wheat, bran, pollard, canola, soy, salt, sodium bicarbonate, bentonite, lime and a vitamin premix (Young Stockfeeds, NSW, Australia). A CSIRO Animal Ethics and Experimentation Committee approved euthanasia and tissue collection from the sample animals; animals were euthanized with an overdose of pentobarbitone sodium (CSIRO Sustainable Ecosystems Animal Ethics Approval Number 06–20). Prior to shipping to the laboratory on dry ice and subsequent storage at −80°C, forestomach contents were transferred to sterile containers containing a glycerol based cryoprotectant as outlined by McSweeney et al. [26].
Enrichment cultures for potential acetogens
Enrichment culture medium was modified from the AC11.1 medium of Greening and Leedle [27] and contained per litre, 38 ml of Mineral solution 2, 38 ml of Mineral solution 3, 200 ml of clarified rumen fluid, 1 ml of Pfennigs trace element solution, 1 ml of haemin solution and 1 ml of resazurin indicator as outlined by McSweeney et al. [26] as well as 1.7 ml acetic acid, 0.6 ml propionic acid, 0.4 ml n-butyric acid, 0.1 ml of each of n-valeric, isovaleric, isobutyric and 2-methylbutyric acid, 2 g of Na2HPO4.2H2O, 6 g of NaHCO3, 0.5 g of yeast extract and 0.25 g of cysteine-HCl. The final pH was adjusted to between 6.4 and 6.8. All media were prepared using standard anaerobic techniques [28], were dispensed in an anaerobic chamber with an atmosphere of 95% CO2 and 5% H2 (COY Laboratory Products Inc., Ann Arbor, MI) and were sterilised by autoclaving at 121°C, 100 kPa for 20 minutes. Modified AC11.1 medium was dispensed either as 9.9 ml aliquots in 27 ml Balch tubes (Bellco, Vineland, NJ) or as 100 ml aliquots in 125 ml serum bottles, both sealed with butyl rubber stoppers (Bellco). Immediately before sample inoculation for enrichment cultures, bromoethane sulfonate (BES; Sigma, Australia) to final concentration 2 mM was added to modified AC11.1 medium to inhibit growth of methanogens.
Glycerol stocks of samples were thawed and approximately 0.1 ml of stored forestomach contents from individual animals were inoculated separately to modified AC11.1 medium with 2 mM BES. Balch tubes were then pressurized with H2:CO2 (4:1) to 150 kPa and incubated horizontally at 39°C. After 2 days of growth 0.1 ml of each culture was pooled and used as inoculum into 9.9 ml of fresh medium in triplicate and incubated as previously. Headspace gas pressures in the cultures were measured regularly using a pressure gauge (Rydalmere, New South Wales, Australia) with a Luer Lock connecter for needle attachment. Gas was refilled as necessary and cultures were grown in this manner for a maximum of five weeks to enrich for hydrogen utilisers. The ratio of gases in the headspace and concentration of SCFA and sulphide ion in the culture supernatant were determined at harvesting.
Chemical analyses
Analysis of headspace gas for hydrogen, carbon dioxide and methane was done by gas chromatography on a Shimadzu GC-2014 (Shimadzu, Kyoto, Japan) fitted with a packed Hayesep Q column (1.8 m × 2.00 mm ID, Valco Instruments Co. Inc., Houston, TX). Nitrogen was the carrier gas at 25 ml min−1 and separation of gases was achieved over a 3 minute period. The temperature of the column oven and the thermal conductivity detector were 38°C and 100°C respectively.
Concentrations of the SCFAs - acetic, propionic, n-butyric, isobutyric, isovaleric and n-valeric acid were determined by flame ionization detection on a Shimadzu GC-2014 with a Zebron™ ZB-FFAP column (30 m x 0.53 mm ID, Phenomenex, Torrance, CA), after acidification with ortho-phosphoric acid and with 4 methyl valeric acid at a final concentration of 1 mM as an internal standard. A 0.5 μl aliquot of each sample was injected; the carrier gas was hydrogen at 5 ml min−1 and separation of the acids was achieved over 13 minutes. The injector and detector temperature were 200°C and 230°C respectively; the column temperature was initially 100°C for 2 minutes followed by a gradient 15°C min −1 to 230°C with a 2 minute hold. Peak detection and chromatogram integration were performed using GCsolution v 3.30.00 (Shimadzu).
Dissolved sulphide was detected by ion chromatography using the method of Keller-Lehman et al. [29].
An UltiMate® 3000 HPLC system (Dionex, Sunnyvale, CA) with a dedicated Photodiode Array Detector and an Autosampler was used to determine the presence of formic, lactic, acetic, citric, succinic and fumaric acids in culture supernatant. A 2.5 μl aliquot of each sample was injected. Separation and identification was achieved using an AcclaimTM Organic Acid (OA) Analytical Column (5 μm, 4.0 x 150 mm, Dionex) at 30°C using a mobile phase of 50 mM NaH2PO4 (pH 2.7) at 0.6 ml min−1 for 7 minutes. Peak analysis was performed using the Chromeleon software (Dionex).
Glycerol and its derivative 1,3-propanediol were analysed by HPLC as described by Keller-Lehman (pers. comm.). Briefly, 20 μl of each sample was injected on a Phenomenex Rezex ROA-Organic acid H+ column (7.8 x 300 mm) using 0.008 N H2SO4 as mobile phase at 0.6 ml min−1 and 35°C column temperature. A Shimadzu 10A HPLC system with an autoinjector and a degasser was used; samples were detected with a refractive index detector (RID-10A) and analysed using CLASS VP software (Shimadzu).
Potential alcohols produced from glycerol fermentation (ethanol, propanol and n-butanol) were analysed on an Agilent 7890A GC (Agilent Technologies) using a capillary column, DB-FFAP (Agilent, 15 m length x 0.53 mm ID x 1.0 μm film) and an FID detector; high-purity helium with an initial flow of 12.5 ml min−1 was used as carrier gas. A 0.5 μl aliquot of each sample was injected at 220°C injection port temperature; the column temperature was 60°C with a hold for 2 minutes, followed by a gradient of 20°C min−1 to 240°C (2 minute hold) with a run time of 13 minutes. The FID detector temperature was at 250°C and analysis was done on Agilent GC ChemStation software.
DNA extraction and molecular analyses of rrs, acsB and fhs
DNA was extracted from enrichment cultures using the cetyltrimethylammonium bromide (CTAB) method of Brookman et al. [30] with minor modifications as described previously [8]. Partial rrs sequences were amplified using primers 27f and 1492r [31] and PCR, cloning and sequencing was performed as outlined previously [32]. Potentially chimeric sequences were determined using the chimera detection program at the Ribosomal Database Project II [33] and sequences shorter than 500-bp were removed from further analysis. Partial rrs sequences were aligned using the NAST aligner and classified using the Hugenholtz taxonomy at the Greengenes database [34]. Sequences were grouped into Operational Taxonomic Units (OTUs) using MOTHUR [35] and a distance ≤ 0.025 to group sequences at an approximate species level [36]. Partial rrs sequences (n = 96) from tammar wallaby forestomach enrichment cultures have been submitted to the GenBank [KF264051 to KF264147].
Functional gene (formyltetrahydrofolate synthetase, fhs and acetyl-CoA synthase, acsB) based analyses of acetogens were performed using partial acsB amplified from enrichment culture DNA using the primers ACS_f and ACS_r and protocol of Gagen et al. [8]. Amplicons were cloned as above and sequenced with vector primers T7 and SP6 (Promega). Partial fhs were amplified using the primers and protocol of Leaphart & Lovell [37] and clone libraries were constructed as for acsB sequences. Deduced amino acids of acsB (ACS) and of the formyl-tetrahydrofolate synthetase (fhs) (FTHFS) were aligned in ARB [38] with publicly available sequences and grouped into Operational Taxonomic Units (OTUs) at a distance of ≤ 0.035 for ACS and ≤ 0.025 for FTHFS, to cluster similar sequences while separating those from distinct species [8]. Maximum likelihood trees of deduced ACS or FTHFS amino acid sequences were constructed as outlined previously [8] using RaxML [39] at the CIPRES portal [40] and the Jones Taylor Thornton [41] model of amino acid substitutions with a gamma rate of substitution and 25 discrete rate categories. Bootstrap analysis was performed for the best-scoring tree topology with 100 resamplings, using RaxML [39]. FTHFS sequences were assessed for similarity to FTHFSs from authentic acetogens using the HS score of Henderson et al. [42]. Putative fhs sequences recovered in this study (n = 64) have been submitted to GenBank [JN1972107 to JN197271]. Putative acsB sequences recovered in this study (n = 41) have been submitted to GenBank [JN197042 to JN197082].
Isolation of acetogens from enrichment cultures
Isolation of potential acetogens (heterotrophic/autotrophic) was carried out in an anaerobic chamber of atmosphere CO2:H2 (95:5) by a 10-fold serial dilution of actively growing enrichment cultures to 10−8. To a 2 ml aliquot of each of these dilutions an equal volume of 2% low melting point agarose in modified AC11.1 containing 2.5 g of glucose, 2.5 g of cellobiose was added at approximately 40°C. This agarose/bacterial mix was poured as an overlay onto modified AC11.1 agar plates and allowed to solidify before being incubated at 39°C in a 3.4 L anaerobic jar (Oxoid Ltd, Cambridge, UK) with the atmosphere of the anaerobic chamber before addition of H2 to 30 kPa overpressure. Glucose and cellobiose were included in the agar overlay to stimulate growth and aid colony formation of acetogens that had been enriched on the previous, limiting medium; few colonies formed on solid medium without added organics.
Single colonies that appeared on or in the agar after one week were picked in an anaerobic hood (atmosphere as above) into 1 ml of liquid modified AC11.1 medium in 1.6 ml round 96-well deep well plates (Axygen, Union City, CA). The 96-well deep well plates were sealed with Airpore™ (Qiagen, Hilden, Germany) plate sealer and incubated at 39°C inside the anaerobic chamber. After three days, cultures from this original plate were inoculated (1:50) into fresh medium in 96-well deep well plates as replicates and grown as before. Crude DNA was extracted from the original plate by the following method: the 96-well deep well plates were centrifuged at 6000 g for 20 minutes at 4°C and the supernatant discarded; approximately 200 mg of a 1:1 mixture of 0.1 mm and 1.0 mm silica-zirconium beads (Biospec, Bartlesville, OK) and 1 ml of TE buffer (10 mM Tris, 1 mM EDTA) were added to each well. Samples were homogenized in a Retsch® Mixer Mill MM 300 (Retsch, Haan, Germany) fitted with an adapter for 96-well plates (Qiagen) at maximum speed for 2 minutes. After centrifugation, 100 μl of the supernatant containing DNA was transferred to a new 96-well PCR plate, heated at 80°C for 20 minutes and 1 μl of this lysate used in a PCR to screen for the presence of the fhs gene using the primers and protocol of Leaphart & Lovell [37] at a modified annealing temperature of 52°C. Cultures from the replicate 96-well deep wells corresponding to fhs positive PCRs were inoculated into modified AC11.1 medium in Balch tubes, pressurised with 150 kPa 4:1 H2:CO2 and monitored for hydrogen consumption.
Preliminary investigation of tammar wallaby forestomach acetogen
Potential acetogens from the tammar wallaby forestomach enrichment cultures were further purified by streaking on agar plates and picking single colonies. Three potential acetogen isolates obtained were almost identical at the rrs level, therefore detailed analyses were only performed on one isolate, arbitrarily named isolate TWA4. Isolate TWA4 was grown horizontally in triplicate at 39°C in modified AC11.1 medium with vitamins (vitamin solution from the DSMZ Medium 141 http://www.dsmz.de/microorganisms/medium/pdf/DSMZ_Medium141.pdf) under 150 kPa 4:1 H2:CO2 and tubes laid horizontally with gentle shaking at 40 rpm on a gyratory shaker. The purity of isolate TWA4 was checked by microscopy and confirmed by the absence of any mixed chromatograms peaks when the 27f/1492r 16S rDNA PCR product was directly sequenced with each of the primers 27f, 519r, 530f, 907r and 1492r [31]. Hydrogen utilisation, SCFA and organic acid production were determined by GC and HPLC as outlined above. DNA from isolate TWA4 cultures was extracted as outlined above and rrs, fhs and acsB were amplified and analysed as for enrichment cultures. Additionally, longer acsB fragments from isolate TWA4 were obtained by PCR with primer combinations ACSF1 with ACSR1 [8] and ACS851F (5′-GGMTTCCCDGYHRTNACHRA-3′) with ACS_r; the latter primer pair was used with a final concentration of 0.4 mg ml−1 bovine serum albumin (New England Biolabs, Ipswich, MA) in PCR as follows: initial denaturation at 95°C for 5 min; 35 cycles of denaturation at 95°C for 30 s; annealing at 48°C for 30 s; and extension at 72°C for 1 min and 30 s; final extension at 72°C for 7 min. the fhs, acsB and rrs sequences from isolate TWA4 have been deposited at GenBank [JN197085-JN197086, JN197083-JN197084 and JN196964 respectively].
Microscopic analyses
Isolate TWA4 cell morphology was investigated by phase-contrast and electron microscopy. The Gram reaction of isolate TWA4 was determined by conventional Gram staining [43] and the KOH test [44]. The structure of the cell wall of isolate TWA4 was determined by transmission electron microscopy (TEM) after high pressure freezing and freeze substitution in osmium tetroxide-uranyl acetate in acetone as outlined by McDonald and Webb [45]. Thin sections were stained with uranyl acetate and lead citrate [46] and visualised using a JEOL 1010 transmission electron microscope (Jeol Ltd., Tokyo, Japan).
Investigation of mixotrophic abilities of isolate TWA4
In preliminary investigations a range of carbon sources and electron acceptors were tested as additives to modified AC11.1 medium with H2:CO2 to determine whether isolate TWA4 was capable of mixotrophic growth. Early indications were that glycerol appeared to stimulate acetate production and cell densities of isolate TWA4 while hydrogen consumption continued, therefore this substance was investigated in more detail. Isolate TWA4 was grown in triplicate as 100 ml cultures in 185 ml bottles on modified AC11.1 medium with (i) H2:CO2 (4:1, 145 kPa) (ii) glycerol (10 mM) and H2:CO2 (4:1, 145 kPa) or (iii) glycerol (10 mM) alone (with the headspace atmosphere as remaining after dispensing in an anaerobic chamber). Headspace gas pressures were monitored by pressure sensors and hydrogen and SCFA concentrations were determined at time zero and every six hours for up to 54 hours.
Co-culture of isolate TWA4 with a methanogen
In order to investigate the hydrogen threshold and hydrogenotrophic ability of isolate TWA4 in comparison with a methanogen, co-culture experiments were performed with isolate TWA4 and M. smithii PS (ATCC 35061). M. smithii was chosen from a panel of methanogens for its ability to grow at the same temperature, a similar growth rate and in the same medium as isolate TWA4. With the addition of a further 1.5 g L−1 yeast extract to modified AC11.1 medium both isolate TWA4 and M. smithii grew robustly; this modified medium used in co-culture experiments is referred to as modified AC11.1Y medium. Isolate TWA4 and M. smithii were grown separately on modified AC11.1Y medium to an OD600 of 0.2, or diluted to this OD (M. smithii only). An equal volume (1:100 each) of these cultures was inoculated, in an anaerobic hood (atmosphere as previously) for co-culture studies. Cultures were performed in triplicate in 10 ml media in 27 ml Balch tubes under autotrophic conditions (i.e. modified AC11.1Y with H2:CO2 (4:1) at 131.5 kPa) or heterotrophic conditions (modified AC11.1Y medium with glycerol at a final concentration of 10 mM and headspace as per the anaerobic chamber atmopshere) and included (i) isolate TWA4 alone (ii) M. smithii alone and (iii) a co-culture of isolate TWA4 and M. smithii inoculated together. Triplicates of uninoculated medium served as controls.
Statistical analyses
A student’s t-test was used to compare differences of means. Differences were considered significant at p < 0.05.
Genome sequencing
Isolate TWA4 was grown in 500 ml of modified AC11.1Y medium with H2:CO2 (4:1) provided at 150 kPa, in a 1 L anaerobic bottle (Bellco). Cells were harvested (6000 g, 15 min, 4°C) after approximately 72 h growth (culture optical density at 600 nm ~0.20) and DNA was extracted by enzymatic lysis as outlined by Pope et al. [47], except also including 60 s bead-beating in a FastPrep®-24 bead-beater (MP Biomedicals, Solon, OH) and incubation at 70°C for 10 minutes prior to chloroform/isoamyl alcohol extraction. The DNA was checked for quality by agarose gel electrophoresis, quantified by Quant-iTTM dsDNA assay kit (Invitrogen, Carlsbad, CA) and sequenced on a Roche/454 FLX sequencer using a shotgun/ 10 kb paired-end sequencing method. Sequence reads were assembled into scaffolds using Newbler version 2.6 and uploaded to the Rapid Annotation using Subsystem Technology (RAST) server for gene calling and annotation [48]. This Whole Genome Shotgun project has been deposited at DDBJ/EMBL/Genbank under the accession JPZU00000000. The version described in this paper is version JPZU01000000.
Acknowledgments
We thank Lyn Hinds, CSIRO Division of Entomology, Black Mountain for providing tammar wallaby forestomach samples. Emma Gagen was a recipient of scholarships from The University of Queensland and CSIRO Livestock Industries. This work was partly supported by Meat and Livestock Australia, The Australian Government Department of Agriculture, Fisheries and Forestry Carbon Farming Futures Filling the Research Gap Program and the former Australian Greenhouse Office. The authors acknowledge the facilities, and the scientific and technical assistance, of the Australian Microscopy & Microanalysis Research Facility at the Centre for Microscopy and Microanalysis, The University of Queensland.
Additional files
Footnotes
Emma J Gagen and Jiakun Wang contributed equally to this work.
Competing interests
The authors declare that they have no competing interests.
Authors’ contributions
EG prepared enrichment cultures and carried out functional gene analyses, participated in characterisation of isolate TWA4 and statistical analyses and drafted the manuscript. JW characterised autotrophic and mixotrophic growth properties of isolate TWA4 and contributed to the drafting of the manuscript. JP participated in isolation and characterisation of isolate TWA4 and co-cultures. JingL participated in characterising the mixotrophic growth properties of isolate TWA4. IC participated in the characterisation of isolate TWA4 and co-cultures with a methanogen. JianxinL was the mentor and supervisor of JW and the PhD student JingL. RW performed electron microscopic analysis of isolate TWA4. RAJ was the supervisor of the PhD student EG. MM conceived of the initial study to examine hydrogenotrophy in the tammar wallaby foregut for comparative work with ruminants. SD undertook sequencing and assembly of the genome of isolate TWA4, contributed to the design of the study and helped draft the manuscript. CM conceived of the study, participated in its design and coordination and helped draft the manuscript. All authors read and approved the final manuscript.
Contributor Information
Emma J Gagen, Email: emma.gagen@gmail.com.
Jiakun Wang, Email: jiakunwang@zju.edu.cn.
Jagadish Padmanabha, Email: jagadish.padmanabha@csiro.au.
Jing Liu, Email: jliu327@163.com.
Isabela Pena Carvalho de Carvalho, Email: Isabela.Carvalho@nutreco.com.
Jianxin Liu, Email: liujx@zju.edu.cn.
Richard I Webb, Email: r.webb@uq.edu.au.
Rafat Al Jassim, Email: r.aljassim@uq.edu.au.
Mark Morrison, Email: m.morrison1@uq.edu.au.
Stuart E Denman, Email: stuart.denman@csiro.au.
Christopher S McSweeney, Email: chris.mcsweeney@csiro.au.
References
- 1.Moss AR, Jouany J-P, Newbold J. Methane production by ruminants: its contribution to global warming. Ann Zootech. 2000;49:231–253. doi: 10.1051/animres:2000119. [DOI] [Google Scholar]
- 2.Thorpe A. Enteric fermentation and ruminant eructation: the role (and control?) of methane in the climate change debate. Clim Change. 2009;93:407–431. doi: 10.1007/s10584-008-9506-x. [DOI] [Google Scholar]
- 3.Johnson KA, Johnson DE. Methane emissions from cattle. J Anim Sci. 1995;73:2483–2492. doi: 10.2527/1995.7382483x. [DOI] [PubMed] [Google Scholar]
- 4.Kempton TJ, Murray RM, Leng RA. Methane production and digestibility measurements in the grey kangaroo and sheep. Aust J Biol Sci. 1976;29:209–214. doi: 10.1071/bi9760209. [DOI] [PubMed] [Google Scholar]
- 5.Dellow DW, Hume ID, Clarke RTJ, Bauchop T. Microbial activity in the forestomach of free-living macropodid marsupials: comparisons with laboratory studies. Aust J Zool. 1988;36:383–395. doi: 10.1071/ZO9880383. [DOI] [Google Scholar]
- 6.von Engelhardt W, Wolter S, Lawrenz H, Hemsley JA. Production of methane in two non-ruminant herbivores. Comp Biochem Physiol. 1978;60:309–311. doi: 10.1016/0300-9629(78)90254-2. [DOI] [Google Scholar]
- 7.Attwood G, McSweeney CS. Methanogen genomics to discover targets for methane mitigation technologies and options for alternative H2 utilisation in the rumen. Aust J Exp Agric. 2008;48:28–37. doi: 10.1071/EA07203. [DOI] [Google Scholar]
- 8.Gagen EJ, Denman SE, Padmanabha J, Zadbuke S, Al Jassim R, Morrison M, McSweeney CS. Functional gene analysis suggests different acetogen populations in the bovine rumen and tammar wallaby forestomach. Appl Environ Microbiol. 2010;76:7785–7795. doi: 10.1128/AEM.01679-10. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9.Ouwerkerk D, Maguire AJ, Klieve AV. Reductive Acetogenesis in the Foregut of Macropod Marsupials in Australia. In: Soliva CR, Takahashi J, Kreuzer M, editors. 2nd International Conference on Greenhouse Gases and Animal Agriculture 20–24 Sep. 2005; Zurich, Switzerland. Amsterdam: Elsevier; 2006. pp. 98–101. [Google Scholar]
- 10.Ouwerkerk D, Maguire AJ, McMillen L, Klieve AV. Hydrogen utilising bacteria from the forestomach of eastern grey (Macropus giganteus) and red (Macropus rufus) kangaroos. Anim Prod Sci. 2009;49:1043–1051. doi: 10.1071/EA08294. [DOI] [Google Scholar]
- 11.Pierce E, Xie G, Barabote RD, Saunders E, Han CS, Detter JC, Richardson P, Brettin TS, Das A, Ljungdahl LG, Ragsdale SW. The complete genome sequence of Moorella thermoacetica (f. Clostridium thermoaceticum) Environ Microbiol. 2008;10:2550–2573. doi: 10.1111/j.1462-2920.2008.01679.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.da Silva GP, Mack M, Jonas C. Glycerol: a promising and abundant carbon source for industrial microbiology. Biotechnol Adv. 2009;27:30–39. doi: 10.1016/j.biotechadv.2008.07.006. [DOI] [PubMed] [Google Scholar]
- 13.Breznak JA, Blum JS. Mixotrophy in the termite gut acetogen, Sporomusa termitida. Arch Microbiol. 1991;156:105–110. doi: 10.1007/BF00290981. [DOI] [Google Scholar]
- 14.Morvan B, Fonty G. Mixotrophy by rumen acetogenic bacteria in the utilization of hydrogen and sugars. Ann Zootech. 1996;45:354. doi: 10.1051/animres:19960683. [DOI] [Google Scholar]
- 15.Joblin KN. Ruminal acetogens and their potential to lower ruminant methane emissions. Aust J Agric Res. 1999;50:1307–1313. doi: 10.1071/AR99004. [DOI] [Google Scholar]
- 16.Drake HL, Gößner AS, Daniel SL. Old acetogens, new light. Ann N Y Acad Sci. 2008;1125:100–128. doi: 10.1196/annals.1419.016. [DOI] [PubMed] [Google Scholar]
- 17.Maru BT, Bielen AAM, Constanti M, Medina F, Kengen SWM. Glycerol fermentation to hydrogen by Thermotoga maritima: Proposed pathway and bioenergetic considerations. Int J Hydrogen Energy. 2013;38:5563–5572. doi: 10.1016/j.ijhydene.2013.02.130. [DOI] [Google Scholar]
- 18.Ellis JL, Dijkstra J, Kebreab E, Bannink A, Odongo NE, McBride BW, France J. Aspects of rumen microbiology central to mechanistic modelling of methane production in cattle. J Agr Sci. 2008;146:213–233. doi: 10.1017/S0021859608007752. [DOI] [Google Scholar]
- 19.Ungerfeld EM, Kohn RA. The Role of Thermodynamics in the Control of Ruminal Fermentation. In: Sejrsen K, Hvelpund T, Nielsen MO, editors. Ruminant Physiology: Digestion, Metabolism and Impact of Nutrition on Gene Expression, Immunology and Stress. Wageningen, The Netherlands: Wageningen Academic Publishers; 2004. pp. 55–85. [Google Scholar]
- 20.Fonty G, Joblin KN, Chavarot M, Roux R, Naylor GE, Michallon F. Methanogen-free lambs: establishment and development of ruminal hydrogenotrophs. Appl Environ Microbiol. 2007;73:6391–6403. doi: 10.1128/AEM.00181-07. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Mitsumori M, Matsui H, Tajima K, Shinkai T, Takenaka A, Denman SE, McSweeney CS. Effect of bromochloromethane and fumarate on phylogenetic diversity of the formyltetrahydrofolate synthetase gene in bovine rumen. Anim Sci J. 2014;85:25–31. doi: 10.1111/asj.12072. [DOI] [PubMed] [Google Scholar]
- 22.Morvan B, Rieu-Lesme F, Fonty G, Gouet P. In vitro interactions between rumen H2-producing cellulolytic microorganisms and H2-utilizing acetogenic and sulfate-reducing bacteria. Anaerobe. 1996;2:175–180. doi: 10.1006/anae.1996.0023. [DOI] [Google Scholar]
- 23.Nollet L, Demeyer D, Verstraete W. Effect of 2-bromoethansulfonic acid and Peptostreptococcus productus ATCC 35244 addition on stimulation of reductive acetogensis in the ruminal ecosystem by selective inhibition of methanogenesis. Appl Environ Microbiol. 1997;63:194–200. doi: 10.1128/aem.63.1.194-200.1997. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Evans PN, Hinds LA, Sly L, McSweeney CS, Morrison M, Wright A-DG. Community composition and density of methanogens in the foregut of the Tammar wallaby (Macropus eugenii) Appl Environ Microbiol. 2009;75:2598–2602. doi: 10.1128/AEM.02436-08. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Pope PB, Smith W, Denman SE, Tringe SG, Barry K, Hugenholtz P, McSweeney CS, McHardy AC, Morrison M. Isolation of Succinivibrionaceae implicated in low methane emissions from Tammar wallabies. Science. 2011;333:646–648. doi: 10.1126/science.1205760. [DOI] [PubMed] [Google Scholar]
- 26.McSweeney CS, Denman SE, Mackie RI. Rumen Bacteria. In: Makkar HPS, McSweeney CS, editors. Methods in Gut Microbial Ecology for Ruminants. The Netherlands: Springer; 2005. pp. 23–37. [Google Scholar]
- 27.Greening RC, Leedle JAZ. Enrichment and isolation of Acetitomaculum ruminis, gen. nov., sp. nov.: acetogenic bacteria from the bovine rumen. Arch Microbiol. 1989;151:399–406. doi: 10.1007/BF00416597. [DOI] [PubMed] [Google Scholar]
- 28.Hungate RE. A Roll Tube Method for Cultivation of Strict Anaerobes. In: Norris JR, Ribbons DW, editors. Methods in Microbiology. Volume 3B. New York: Academic Press; 1969. pp. 117–132. [Google Scholar]
- 29.Keller-Lehman B, Corrie SK, Ravn R, Yuan Z, Keller J. Preservation and Simultaneous Analysis of Relevant Soluble Sulfur Species in Sewage Samples. In: Ertl T, Pressl A, Kretschmer F, Haberl R, editors. 2nd International IWA Conference on Sewer Operation and Maintenance: 26–28 Oct; Vienna, Austria. Austria: SIG Eigenverlag; 2006. pp. 339–346. [Google Scholar]
- 30.Brookman JL, Nicholson MJ. Anaerobic Fungal Populations. In: Makkar HPS, McSweeney CS, editors. Methods in Gut Microbial Ecology for Ruminants. Netherlands: Springer; 2005. pp. 139–150. [Google Scholar]
- 31.Lane DJ. 16S/23S rRNA Sequencing. In: Stackebrandt E, Goodfellow M, editors. Nucleic Acid Techniques in Bacterial Systematics. London: Wiley; 1991. pp. 115–175. [Google Scholar]
- 32.Gagen EJ, Mosoni P, Denman SE, Al Jassim R, McSweeney CS, Forano E. Methanogen colonisation does not significantly alter acetogen diversity in lambs isolated 17 h after birth and raised aseptically. Microb Ecol. 2012;64:628–640. doi: 10.1007/s00248-012-0024-z. [DOI] [PubMed] [Google Scholar]
- 33.Cole JR, Chai B, Marsh TL, Farris RJ, Wang Q, Kulam SA, Chandra S, McGarrell DM MST, Garrity GM, Tiedje JM. The Ribosomal Database Project (RDP-II) previewing a new autoaligner that allows regular updates and the new prokaryotic taxonomy. Nucleic Acids Res. 2003;31:442–443. doi: 10.1093/nar/gkg039. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.DeSantis TZ, Hugenholtz P, Larsen N, Rojas M, Brodie EL, Keller K, Huber T, Dalevi D, Hu P, Andersen GL. Greengenes, a chimera-checked 16S rRNA gene database and workbench compatible with ARB. Appl Environ Microbiol. 2006;72:5069–5072. doi: 10.1128/AEM.03006-05. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Schloss PD, Westcott SL, Ryabin T, Hall JR, Hartmann M, Hollister EB, Lesniewski RA, Oakley BB, Parks DH, Robinson CJ, Sahl JW, Stres B, Thallinger GG, Van Horn DJ, Weber CF. Introducing mothur: open-source, platform-independent, community-supported software for describing and comparing microbial communities. Appl Environ Microbiol. 2009;75:7537–7541. doi: 10.1128/AEM.01541-09. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 36.Stackebrandt E, Goebel BM. Taxonomic note: a place for DNA-DNA reassociation and 16S rRNA sequence analysis in the present species definition in bacteriology. Int J Syst Bacteriol. 1994;44:846–849. doi: 10.1099/00207713-44-4-846. [DOI] [Google Scholar]
- 37.Leaphart AB, Lovell CR. Recovery and analysis of formyltetrahydrofolate synthetase gene sequences from natural populations of acetogenic bacteria. Appl Environ Microbiol. 2001;67:1392–1395. doi: 10.1128/AEM.67.3.1392-1395.2001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38.Ludwig W, Strunk O, Westram R, Richter L, Meier H, Yadhukumar, Buchner A, Lai T, Steppi S, Jobb G, Forster W, Brettske I, Gerber S, Ginhart AW, Gross O, Grumann S, Hermann S, Jost R, Konig A, Liss T, Lussmann R, May M, Nonhoff B, Reichel B, Strehlow R, Stamatakis A, Stuckmann N, Vilbig A, Lenke M, Ludwig T, et al: ARB: a software environment for sequence data.Nucleic Acids Res 2004, 32:1363–1371. [DOI] [PMC free article] [PubMed]
- 39.Stamatakis A. RAxML-VI-HPC: Maximum likelihood-based phylogenetic analyses with thousands of taxa and mixed models. Bioinformatics. 2006;22:2688–2690. doi: 10.1093/bioinformatics/btl446. [DOI] [PubMed] [Google Scholar]
- 40.Miller MA, Pfeiffer W, Schwartz T. Proceedings of the Gateway Computing Environments Workshop (GCE): 14 Nov. 2010. New Orleans, LA: IEEE; 2010. Creating the CIPRES Science Gateway for Inference of Large Phylogenetic Trees; pp. 1–8. [Google Scholar]
- 41.Jones DT, Taylor WR, Thornton JM. A new approach to protein fold recognition. Nature. 1992;358:86–89. doi: 10.1038/358086a0. [DOI] [PubMed] [Google Scholar]
- 42.Henderson G, Naylor GE, Leahy SC, Janssen PH. Presence of novel, potentially homoacetogenic bacteria in the rumen as determined by analysis of formyltetrahydrofolate synthetase sequences from ruminants. Appl Environ Microbiol. 2010;76:2058–2066. doi: 10.1128/AEM.02580-09. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Sambrook J, Russell DW. Molecular Cloning: A Laboratory Manual. 3. New York: Cold Spring Harbor Laboratory Press; 2001. [Google Scholar]
- 44.Buck JD. Nonstaining (KOH) method for determination of Gram reactions of marine bacteria. Appl Environ Microbiol. 1982;44:992–993. doi: 10.1128/aem.44.4.992-993.1982. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.McDonald KL, Webb RI. Freeze substitution in 3 hours or less. J Microsc. 2011;243:227–233. doi: 10.1111/j.1365-2818.2011.03526.x. [DOI] [PubMed] [Google Scholar]
- 46.Reynolds ES. The use of lead citrate at high pH as an electron-opaque stain in electron microscopy. J Cell Biol. 1963;17:208–212. doi: 10.1083/jcb.17.1.208. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 47.Pope PB, Denman SE, Jones M, Tringe SG, Barry K, Malfatti SA, McHardy AC, Cheng J-F, Hugenholtz P, McSweeney CS, Morrison M. Adaptation to herbivory by the Tammar wallaby includes bacterial and glycoside hydrolase profiles different from other herbivores. Proc Natl Acad Sci U S A. 2010;107:14793–14798. doi: 10.1073/pnas.1005297107. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48.Aziz RK, Bartels D, Best AA, DeJongh M, Disz T, Edwards RA, Formsma K, Gerdes S, Glass EM, Kubal M, Meyer F, Olsen GJ, Olson R, Osterman AL, Overbeek RA, McNeil LK, Paarmann D, Paczian T, Parrello B, Pusch GD, Reich C, Stevens R, Vassieva O, Vonstein V, Wilke A, Zagnitko O. The RAST server: rapid annotations using subsystems technology. BMC Genomics. 2008;9:75. doi: 10.1186/1471-2164-9-75. [DOI] [PMC free article] [PubMed] [Google Scholar]