- Open Access
The effects of CO2 and H2 on CO metabolism by pure and mixed microbial cultures
Biotechnology for Biofuels volume 10, Article number: 220 (2017)
Syngas fermentation, the bioconversion of CO, CO2, and H2 to biofuels and chemicals, has undergone considerable optimization for industrial applications. Even more, full-scale plants for ethanol production from syngas fermentation by pure cultures are being built worldwide. The composition of syngas depends on the feedstock gasified and the gasification conditions. However, it remains unclear how different syngas mixtures affect the metabolism of carboxidotrophs, including the ethanol/acetate ratios. In addition, the potential application of mixed cultures in syngas fermentation and their advantages over pure cultures have not been deeply explored. In this work, the effects of CO2 and H2 on the CO metabolism by pure and mixed cultures were studied and compared. For this, a CO-enriched mixed culture and two isolated carboxidotrophs were grown with different combinations of syngas components (CO, CO:H2, CO:CO2, or CO:CO2:H2).
The CO metabolism of the mixed culture was somehow affected by the addition of CO2 and/or H2, but the pure cultures were more sensitive to changes in gas composition than the mixed culture. CO2 inhibited CO oxidation by the Pleomorphomonas-like isolate and decreased the ethanol/acetate ratio by the Acetobacterium-like isolate. H2 did not inhibit ethanol or H2 production by the Acetobacterium and Pleomorphomonas isolates, respectively, but decreased their CO consumption rates. As part of the mixed culture, these isolates, together with other microorganisms, consumed H2 and CO2 (along with CO) for all conditions tested and at similar CO consumption rates (2.6 ± 0.6 mmol CO L−1 day−1), while maintaining overall function (acetate production). Providing a continuous supply of CO by membrane diffusion caused the mixed culture to switch from acetate to ethanol production, presumably due to the increased supply of electron donor. In parallel with this change in metabolic function, the structure of the microbial community became dominated by Geosporobacter phylotypes, instead of Acetobacterium and Pleomorphomonas phylotypes.
These results provide evidence for the potential of mixed-culture syngas fermentation, since the CO-enriched mixed culture showed high functional redundancy, was resilient to changes in syngas composition, and was capable of producing acetate or ethanol as main products of CO metabolism.
Microbial anaerobic conversion of CO or synthesis gas (syngas), a gas mixture mainly composed of CO, H2, and CO2, leads to the production of important industrial products, such as acetic and butyric acid, and biofuels, such as ethanol, butanol, H2, and methane [1,2,3,4]. Pure cultures, mainly Clostridium spp. and other Clostridia, have been widely utilized in the study of CO and syngas conversion to ethanol and acetate [5,6,7,8,9,10,11]. Stoichiometric reactions for microbial conversion of CO and syngas to acetic acid and ethanol are summarized in Table 1; Eqs. 1–7.
Efforts to enhance CO and syngas conversion by carboxidotrophic microorganisms to preferred industrial products (e.g., ethanol or acetate) include optimization of nutrients [12, 13], optimization of pH and temperature [14, 15], optimization of bioreactor configuration [5, 9, 16, 17], and metabolic engineering for increased production [8, 18]. However, syngas composition varies depending on the feedstock gasified and the gasification conditions [19, 20]. Hence, different syngas compositions, including CO:CO2, CO:H2, and CO:CO2:H2 at different ratios with or without a source of organic carbon (e.g., yeast extract), varies in most studies [6, 15, 21,22,23,24], making it difficult to understand how CO2, H2, and different syngas mixtures affect CO oxidation and product distribution (e.g., ethanol/acetate ratios).
The available literature on this subject shows that growth of carboxidotrophic acetogens and the ethanol/acetate ratio are influenced by CO2 [7, 25,26,27,28]. In particular, several carboxidotrophs, including Clostridium carboxidivorans, do not grow with CO in the absence of CO2 in certain conditions . Moreover, increasing the CO partial pressure (PCO) and the CO/CO2 ratio resulted in increased average cell concentration and increased ethanol/acetate ratio in C. carboxidivorans P7 . Likewise, increased syngas pressure promoted ethanol production in Clostridium ljungdahlii . Increased PCO, CO/CO2, or syngas pressure promoted ethanol production, possibly because more electrons as CO and/or H2 were available for reduction reactions. As seen in Eqs. 2–7 of Table 1, ethanol production requires more electrons as CO and H2 than acetate production.
The effect of H2 on CO fermentation has been less studied . Although the conversion of CO and H2 to acetate or ethanol is thermodynamically feasible (Eqs. 4–5), only a few reports document pure cultures simultaneously consuming H2 and CO [29,30,31], mainly because CO inhibits hydrogenases [26, 32]. Accordingly, sustainable syngas conversion by pure cultures poses a challenge of keeping an optimal syngas composition in order to assure CO, H2, and CO2 consumption and the desired products ratio.
Mixed cultures are known to have functional redundancy and be more resilient to changes in the environment . Moreover, industrial mixed-culture fermentation might be less costly than pure culture fermentation, as sterile conditions are not as stringent. Despite these potential advantages, little attention has been given to the use of mixed cultures for syngas fermentation [27, 34,35,36]. Similar to pure cultures, syngas components may have effects on the productivity of mixed cultures. Whether or not these effects are similar to the effects of syngas composition on pure cultures remains to be elucidated.
In this work, we studied and compared CO consumption rates and functionality of CO-consuming pure and mixed cultures during fermentation of CO and CO-rich mixtures commonly used in syngas studies (CO:CO2, CO:H2, and CO:CO2:H2). We grew a CO-enriched mixed culture and two carboxidotrophs isolated from it with the same CO-rich gas mixtures and similar conditions. We hypothesized that the addition of CO2 and/or H2 to CO fermentation would alter the metabolism of carboxidotrophs, regarding CO consumption rates and product formation, and that the pure cultures would be more susceptible to changes in gas composition than the mixed culture. In addition, we tested the capability of the CO-enriched mixed culture to switch from acetate to ethanol production by increasing the availability of electrons (as CO), which should promote reduction reactions. We carried out these experiments at neutral pH and in a batch reactor with continuous CO supply through diffusive membranes.
CO-enriched mixed culture and isolation of carboxidotrophs
A CO-enriched mixed culture was obtained by exposing anaerobic sludge to CO as the sole carbon and energy source. Details on the enrichment process were previously published . Isolates namely SVCO-15 (GenBak KY992591) and SVCO-16 (GenBank KY992590) were obtained from the CO-enriched culture .
Growth with CO and different CO-rich gas mixtures by pure and mixed cultures
1 mL of a CO-consuming culture (mixed or pure isolate) in exponential growth was used to inoculate glass serum bottles (160 mL) with 50 mL reduced anaerobic medium and different substrates: CO, CO:CO2, CO:H2, CO:CO2:H2, or CO:yeast extract (YE). Before inoculation, serum bottles were autoclaved for 1 h at 121 °C. Medium was buffered with sodium phosphate (Na2HPO4) and potassium phosphate (KH2PO4) in cultures growing with CO, CO:H2, and CO:YE, and it was buffered with sodium bicarbonate (NaHCO3) in cultures growing with CO:CO2 and CO:CO2:H2. The initial pH in this set of experiments with different gas compositions was 7.3 ± 0.4. The compositions of phosphate- and bicarbonate-buffered media were similar to those described in [38, 39], except that FeCl2 and Na2SO4 were not added, and the trace mineral solution was ATCC Trace Mineral Supplement (Catalog No. MD-TMS). Fermentation of CO also was studied in medium not buffered to allow the pH to decrease. The composition of the non-buffered medium (pH = 7.5 ± 0.1) was similar in composition to the phosphate-buffered medium, except that phosphate salts were not added. All media were reduced with l-cysteine (0.4 mM) and Na2S (0.2 mM) and supplemented with Wolfe’s vitamin solution (ATCC, Vitamin Supplement, catalog no. MD-VS), 0.01% (v v−1). Resazurin was used as an O2 indicator at a concentration of 5 × 10−5% (w v−1).
Serum bottles were incubated at 30 °C and shaken horizontally at 125 rpm to increase CO dissolution. Ultra high pure CO (99.9% purity) and H2, N2:CO2 (80:20), and pre-mixed CO:CO2:H2 (40:30:30) (Praxair, Danbury, CT) were used to feed the cultures. Preparation of gaseous substrates and final ratios of each mixture were as described by Esquivel-Elizondo et al. . The initial total pressure of the serum bottles was 147 kPa (1.45 atm). Every condition was tested in triplicate.
Fermentation of CO in batch reactor with continuous CO supply
The setup of the batch reactor is illustrated in Additional file 1: Figure S1. 32 composite hollow-fiber membranes (Mitsubishi Rayon, Model MHF 200TL) (1.31 cm mL−1) were used to supply CO (at ≤30.4 kPa) by diffusion directly to the liquid media. The CO delivery rate was 12 ± 0.5 μmol h−1, estimated from the amounts of measured end-products. The total volume of the batch reactors was 230 mL, and the liquid was 50 mL of reduced phosphate-buffered medium. Prior to inoculation with 2 mL of the CO-enriched mixed culture derived from sludge, reactors were sparged with N2 (UHP, Praxair) for 10 min and sealed with butyl rubber and aluminum crimps. The batch reactors were placed on a stir-bar hot plate (VWR, #97042-642) operated at 32 ± 1 °C and 150 rpm. Initial partial pressure of CO in the headspace of the reactor was 0 kPa.
Gases in the headspace and fatty acids and alcohols in the liquid phase were detected and quantified via gas and liquid chromatography, respectively, as previously described [37, 40]. Partial pressures were determined with Dalton’s Law of partial pressures: P = % gas in headspace (estimated through gas chromatography) × total pressure in the batch reactor (measured with an electronic gauge manometer). pH values were measured with a pH Benchtop Meter (Thermo Scientific, #9142BN). Organic matter was estimated by quantifying the chemical oxygen demand (COD) in 2 mL samples with COD vial tests (Hach, LR and HR TNTplus vial tests).
DNA extraction and molecular biology analyses
Pellets made by centrifuging 1.5 mL sample at 13,200 rpm for 20 min using a micro-centrifuge 5415 D (Eppendorf, Hauppauge, NY) were used for DNA extraction. To increase total biomass and DNA yield, replicate pellets (stored at −80 °C) were thawed and combined for DNA extraction . Prior to inoculation of serum bottles, the 16S rRNA gene of isolates SVCO-15 and SVCO-16 was directly amplified from genomic DNA for Sanger sequencing using the primer set 8F/1525R, and the PCR conditions are described in . The PCR products were purified and directly sequenced and aligned as previously described .
The 16S rRNA gene copies present in DNA extracted from cultures were quantified via quantitative real-time PCR (qPCR) using the primer set 342F/1492R and the following amplification conditions: pre-denaturation at 95 °C for 10 min; 45 cycles of denaturation at 95 °C for 15 s, and combined annealing and extension at 60 °C for 1 min; an additional cycle of 95 °C for 15 s, and 60 °C for 15 s; and 20 min temperature increase from 60 °C to 95 °C . Each reaction (20 μL) contained: 10 μL of SYBR green mix (Takara, California), 0.2 μL of each forward and reverse primer (10 µM), 8.6 μL water, and 1 μL of template DNA (diluted 100×). Every assay and a six-point standard curve were run in triplicate. The gene copy number per mL was calculated with the following equation:
*Volume of culture (sample) used for DNA extraction. ^Volume of DNA extracted from the sample.
To determine the bacterial community structures for the different conditions, DNA was sequenced using the Illumina MiSeq platform at the Microbiome Analysis Laboratory (http://krajmalnik.environmentalbiotechnology.org/microbiome-lab.html, Arizona State University, Tempe), using Bacterial primers 515F and 806R, which amplify the V4 hyper-variable regions of the 16S rRNA gene , and paired-end, 150 bp reads (2 × 150 mode). Raw sequences were submitted to NCBI Sequence Read Archive and are available under the Project ID PRJNA386595. Forward and reverse sequences were first paired (>45 bp overlap) using PANDASeq . Then, paired reads (average length 253 bp) were processed using the QIIME 1.9.0 pipeline  as described in . The average number of high-quality reads per sample was 43,938 ± 10,513.
Electron balances were performed in order to understand the distribution of electrons from the electron donor(s) (CO, and/or H2) to end-products (acetate, ethanol, H2) . Additional electrons, provided as yeast extract, l-cysteine (used as reducing agent), and biomass (or organic matter), also were considered. These electron balances were quantified as COD using 8 g COD/e− eq. For the electron balances, mmol of electron donors and end-products were converted to electron milliequivalents (e− meq.) using electron equivalents per mole values . The distribution of e− meq. to end-products is reported as a percentage of the initial total e− meq. provided as substrate.
Results and discussion
Addition of H2 and/or CO2 to CO fermentation altered the metabolism of carboxidotrophs
The conversions of CO and CO with H2 and/or CO2 by a CO-enriched mixed culture and two carboxidotrophs isolated from the mixed culture were studied and compared. Based on the 16S rRNA gene partial sequence, the two isolates tested are 99% phylogenetically similar to the acetogen Acetobacterium wieringae and to the N-fixating bacterium Pleomorphomonas diazotrophica . Despite these bacteria having not previously been characterized as carboxidotrophs, sequences mostly similar to A. wieringae were identified in a CO fermenter inoculated with anaerobic digester fluid from a wastewater treatment plant . Additionally, we isolated another strain of A. wieringae from sediments collected close to a lake in Arizona, USA, enriched with CO (GenBank KY992593).
Figures 1 and 2 present the conversion of CO-rich gas mixtures (i.e., CO, CO:CO2:H2, CO:H2, and CO:CO2,) by the CO-enriched mixed culture and the isolates. The mixed culture and the Acetobacterium-like isolate produced H2, CO2, acetate, and ethanol for all conditions tested. However, ethanol production by the Acetobacterium isolate was higher than by the CO-enriched mixed culture. While the isolate produced 0.56 and 0.18 mmol under growth with CO:H2 and CO:CO2, respectively (Fig. 2b, e), the CO enrichment produced 0.08 and 0.02 mmol (Fig. 2a, d). The Pleomorphomonas-like isolate produced H2 and CO2 from CO, according to the water-gas shift reaction (Eq. 1). No other products were detected via gas and liquid chromatography. As presented in Fig. 1d, h, abiotic conversion of CO, CO2, and H2 was negligible.
Opposite to the isolates, which did not completely consume H2, and previous studies with pure cultures, in which H2 was not consumed along with CO (Eqs. 4–5) [26, 28, 48, 49], the CO-enriched mixed culture metabolized H2 along with CO for acetate and ethanol production during growth with CO:CO2:H2 (Fig. 1e) and CO:H2 (Fig. 2a). Since CO dehydrogenase (CODH), the enzyme that catalyzes the reversible reduction of CO to CO2, possesses hydrogenase activity, the activity of hydrogenases in pure cultures of carboxidotrophs could be redundant . However, H2 in syngas could have been consumed through Eqs. 6–7 (Table 1) by hydrogenotrophic microorganisms in the mixed culture. So far, the mesophilic proteobacterium Rubrivivax gelatinosus and the thermophilic Methanothermobacter marburgensis and Thermoanaerobacter kivui are reported to simultaneously utilize CO and H2. More experiments are needed to verify the simultaneous utilization of these substrates [29,30,31].
The presence of CO2 (0.7–1.4 mmol) and H2 (0.7–4.1 mmol) influenced the metabolism of the CO-consuming cultures. As summarized in Table 2, differences in CO consumption rates and ethanol/acetate ratios were observed when the gas components were varied. The pure cultures seemed more sensitive to the addition of H2 and/or CO2 to CO fermentation than the mixed culture. While maximum CO consumption rates (during exponential CO consumption) by the CO-enriched mixed culture were similar under all conditions (2.6 ± 0.6 mmol CO L−1day−1), those achieved by the isolates varied depending on the CO-rich gas mixture (0–5 mmol CO day−1 L−1). Moreover, contrary to the CO-enriched mixed culture, the final 16S rRNA gene copy number, quantified through qPCR, in pure cultures varied by more than one order of magnitude among the different CO-rich gas mixtures. Results from the qPCR analysis are presented and discussed in the supplemental material (Additional file 1: Figure S2).
Production of acetate, ethanol, and/or H2 from CO-rich gases by the CO-consuming cultures is compared in the electron balances presented in Fig. 3. For this, end-products electron equivalents were normalized by the initial electron equivalents in CO and/or H2 and COD in the inoculum, as summarized in Table 2. Figure 3a shows that acetate was the dominant end-product in all fermentations by the CO-enriched mixed culture. More than 72% of the electrons in substrates were utilized for acetate production. Ethanol was produced for all conditions tested, although at smaller proportions: 11 ± 2.3% of the electrons in CO and 2–6% of the electrons in CO with CO2 and/or H2 were directed towards ethanol production. Initial pH was 7.3 ± 0.3, and it decreased to 6.8 ± 0.13 at the end of the experiments. In addition, the final ethanol/acetate ratio was similar for growth with CO2 and H2 as substrates (0.04 ± 0.015 e− meq./e− meq.), and it increased to 0.14 ± 0.03 e− meq./e− meq. for growth with CO as the sole substrate (Table 2). Similarly, estimated ethanol/acetate ratios by an acetogenic mixed culture were 0.37 e− meq./e− meq. at PCO = ~76 kPa (no CO2 added) and decreased to 0.08 and 0.07 e− meq./e− meq. at PCO = 25.3 kPa and PCO and PCO2 of ~25.3 kPa, respectively .
Figure 3b shows that the electron distribution to products by the Acetobacterium-like isolate varied depending on the presence of H2 and/or CO2. The highest distribution of electrons to ethanol was achieved with CO and CO:H2: 54–64% of the electrons in CO:H2 or CO were utilized for ethanol production, whereas less than 33% of the electrons in CO:CO2:H2 and CO:CO2 went to ethanol. The rest of the electrons were distributed to biomass, acetate, and H2, also in different proportions. Similar to the CO-enriched mixed culture, the highest fraction of electrons channeled to acetate by the Acetobacterium-like isolate was achieved with the addition of CO2. Initial medium pH was 7.3 ± 0.3, and it decreased to 7.1 ± 0.0, 7.0 ± 0.1, 7.0 ± 0.1, 6.6 ± 0.2, and 6.8 ± 0.1 after fermentation of CO, CO:YE, CO:H2, CO:CO2, and CO:CO2:H2, respectively. The different final pH values are in accordance with the different ethanol/acetate ratios observed (Table 2); final lower pH corresponded to higher acetate concentrations. Accordingly, ethanol/acetate ratios obtained with growth with CO:CO2 and CO:CO2:H2 were at least 5 times lower (0.86 ± 0.01 and 2.5 ± 0.25 e− meq./e− meq., respectively) than those achieved with CO and CO:H2 (14.2 ± 5.2 and 11.2 ± 0.5 e− meq./e− meq., respectively) (Table 2). These results agree with the results of Heiskanen et al.  and Nam et al. , who report an increase in the acetate production rate and yield with the addition of CO2 to CO fermentation. Ethanol/acetate ratios by the Acetobacterium-like isolate (at total pressures of 147 kPa) growing in syngas (2.5 ± 0.25 e− meq./e− meq.) are higher than those reported for Clostridium ljungdahlii (~0.1–1 e− meq./e− meq.) growing with syngas (55% CO, 10% CO2, 20% H2, 15% Ar) at 101.3–182.4 kPa , but lower to that (~8.5 e− meq./e− meq.) achieved by C. ljungdahlii in a 4-L bioreactor optimized for solventogenesis . In our study, the addition of H2 also promoted acetate production by the CO-enriched mixed culture, but not by the Acetobacterium isolate. A possible explanation is that, while the isolate did not consume most of the H2 provided as substrate (Fig. 2b), the CO-enriched mixed culture consumed H2 along with CO (Fig. 2a), for increased acetate production.
The addition of CO2 and/or H2 to CO fermentation also influenced the metabolism of the Pleomorphomonas-like isolate. CO conversion was highly inhibited by the presence of CO2 in growth with CO:CO2 (PCO2 = 30.4 kPa) and CO:CO2:H2 (PCO2 = 15.2 kPa). More than 70% of the added CO was not consumed after >75 days of fermentation (Figs. 1g, 2f). Exogenous H2 (PH2 = 95.2 kPa) did not inhibit CO consumption, and similar to the CO-enriched mixed culture, it decreased the CO consumption rates, from 1.0 to 0.7 mmol CO L−1 day−1, compared to autotrophic growth with CO as the sole substrate. Correspondingly, the distribution of electrons from CO to H2 was similar (78–81%) in growth with CO and CO:H2, but different than in growth with CO:CO2 and CO:CO2:H2 (Fig. 3c).
Many carboxidotrophs have been observed to require or grow better with yeast extract or similar complex nutrients [13, 51]. The addition of yeast extract (0.05% w v−1) significantly (P < 0.01) increased ethanol production by the Acetobacterium-like isolate, compared to its autotrophic growth with CO as the sole substrate (from 6.6 ± 1.0 to 13.5 ± 3.0 mM). This increase in ethanol production can be seen in Fig. 3b: the distribution of electrons to ethanol increased from 54 ± 11% in growth with CO, to 80 ± 16% in growth with CO and yeast extract, although similar maximum CO consumption rates were achieved: 1.6 ± 0.2 mmol CO L−1 day−1 (Table 2). Acetate production by the Acetobacterium-like isolate grown with CO:YE was not detected (Additional file 1: Figure S3A). Similarly, CO consumption by the Pleomorphomonas-like isolate was stimulated by the addition of yeast extract (0.05% w/v); total CO was consumed in less than half of the time when yeast extract was added (Fig. 1c; Additional file 1: Figure S3B). However, more electrons were provided as substrate with the addition of yeast extract; therefore, more biomass was produced. The higher concentration of biomass was possibly responsible for the shorter lag phase for CO consumption observed in growth with CO:YE compared to CO. However, once microbes were in exponential growth phase, maximum CO conversion rates (1.2 ± 0.2 mmol CO L−1 day−1) were similar (Table 2). As seen in Fig. 3c, the electron distribution to H2 by the Pleomorphomonas-like isolate grown with CO:YE was similar to that observed when grown with CO and CO:H2.
The metabolisms of the Acetobacterium- and Pleomorphomonas-like isolates were affected by changes in syngas composition. CO2 (at PCO2 = 30.4 kPa) inhibited CO oxidation by the Pleomorphomonas isolate and ethanol production by the Acetobacterium isolate. H2 (at PH2 = 91.2 kPa), on the other hand, did not inhibit ethanol or H2 production by the Acetobacterium and Pleomorphomonas isolates, respectively, but decreased their CO consumption rates. These results indicate that the metabolism of these isolates, and possibly of other microorganisms, depends on the syngas composition. Therefore, for industrial applications of non-engineered microorganisms, such as the studied isolates, the feedstock and gasification conditions should be constant in order to fix the syngas composition, and to maintain concentration of the desired end-product(s).
The Acetobacterium and Pleomorphomonas isolates may have been the main carboxidotrophs in the CO-enriched mixed culture that generated H2 and CO2, and acetate and ethanol, respectively, from CO (Figs. 1, 2, 3; Table 2; Additional file 1: Table S1). As part of the mixed culture, these isolates, together with other microorganisms summarized in Additional file 1: Figure S4, consumed CO along with CO2 and H2 at CO consumption rates of 2.6 ± 0.6 mmol CO L−1 day−1. These rates are similar to the ones achieved by thermophilic CO and syngas enrichment cultures (~1.3 – 2.8 mmol CO L−1 day−1 in ) and a mesophilic mixed culture (4 mmol CO L−1 day−1 in ), but lower than the rates achieved by sludge from a wastewater treatment plant treating paper mill (>10 mmol CO L−1 day−1 in ). Ethanol/acetate ratios achieved by the mesophilic CO-enriched mixed culture varied slightly for different combinations of syngas components. Regardless of these ratios and different structures of the microbial communities (Additional file 1: Figure S4), acetate always was the main end-product from CO, CO:CO2, CO:H2, and CO:CO2:H2 (Fig. 3a). Functional redundancy of mixed cultures is important for the sustainable production of acetate and other products from syngas, where the composition of syngas and, therefore, PCO, PCO2, and PH2, constantly vary depending on the type of feedstock gasified (e.g., recalcitrant biomass waste) and the gasification conditions [19, 20].
Ethanol production by the CO-enriched mixed culture increased with continuous CO supply at pH ~7
Since the CO-enriched mixed culture showed advantages for industrial applications over pure cultures (i.e., resiliency to changes in syngas composition, complete syngas consumption at relatively fast CO consumption rates), we further investigated its capacity to produce ethanol over acetate. First, in order to test if a drop in pH would lead to a switch in metabolism from acetate production to ethanol production, as previously reported [15, 25, 35, 53], CO fermentation was carried out in serum bottles with non-buffered medium. The results, presented in Additional file 1: Figure S5, showed that pH decreased from 7.5 ± 0.1 to 6.8 ± 0.1 and that phosphate was necessary for fast CO conversion by the CO-enriched mixed culture, since CO consumption rates in non-buffered medium were slower (1.1 mmol CO day−1 L−1) than rates achieved in phosphate-buffered medium (2.1–3.5 mmol CO day−1 L−1). This agrees with the fact that the CO enrichment culture was enriched with CO in phosphate buffer media . Results on ethanol production, pH values over time, and microbial phylotypes identified in these experiments are presented in the supplemental material.
In order to enhance ethanol production at faster CO consumption rates, fermentation of CO in phosphate-buffered medium (pH 7.5 ± 0.1) was carried out in a batch reactor with continuous CO supply (Additional file 1: Figure S1). The hypothesis tested was that increased availability of electrons (as CO) would increase the reduction potential of the medium, promoting reduction reactions, including ethanol production, to maintain the redox balance. As shown in Fig. 4a and Table 2, acetate and ethanol were produced along fermentation with ethanol/acetate ratios between 0.12 and 0.3 e− meq./e− meq. However, on day 61, a switch from acetate to ethanol production was observed at a pH of 6.9 ± 0.1 (Fig. 4b). Ethanol concentrations increased from 3.4 mM (0.17 mmol) to 69.5 ± 3.1 mM (3.48 ± 0.16 mmol), whereas acetate was no longer detected. This high degree of ethanol production was maintained for 1 more week, until operation of the batch reactor was stopped. Continuous delivery of CO in a batch system increased the availability of electrons for reduction reactions, which promoted the reduction of the C=O group in acetate to a CH2 group to form ethanol. In this regard, increased ethanol production has been observed at higher CO and syngas partial pressures or reducing agent concentrations [6, 10, 25, 53].
As shown in Fig. 4c, the microbial community in the batch reactor with continuous CO supply was distinct from the microbial communities identified in serum bottles with CO and CO-rich mixtures (Additional file 1: Figure S4, S5C), despite being inoculated with the same mixed culture. Phylotypes associated with the acetate producer Geosporobacter (order Clostridiales)  were <0.1% abundant in serum bottles (with buffered and non-buffered media), but dominated the identified microbial community in the batch reactor, both in the liquid phase and in the fibers, after 30 days of fermentation. When the switch from acetate to ethanol production was observed, the relative abundance of Geosporobacter phylotypes, in the liquid phase, increased from 34 to 70%. Porphyromonadaceae (order Bacteroidales) were also detected at high abundance during fermentation with continuous CO supply (2–36%). Phylotypes associated with these acetate producers were also detected in the fermentation of CO and CO-rich gas mixtures in serum bottles, at considerable abundance (up to 4.4%, Additional file 1: Figures S4, S5C). Other phylotypes related to bacteria that ferment acetate became highly abundant in fermentation with continuous CO supply, including the aerobes Achromobacter and Lysinibacillus. These microbes might have been enriched with the small amounts of O2 introduced after sampling, or they might have facultative metabolism. Despite the abundance of these “contaminating” microorganisms, ethanol concentrations and CO consumption rates were high, underscoring the advantages of using mixed microbial communities for robust industrial applications. In summary, increasing the number of electrons (as CO) directly delivered to microorganisms increased ethanol production at neutral pH, and promoted a different microbial community structure, compared to CO fermentation in serum bottles.
Addition of H2 and CO2 during CO fermentation affected the metabolism of the carboxidotrophs. Pure cultures obtained from a CO-enriched mixed culture were more sensitive to changes in syngas components than the CO-enriched mixed culture. The mixed culture showed several advantages over the pure cultures as it adjusted to changes in syngas components and consumed CO along with H2 and CO2. While acetate was the main end-product in serum bottles with a single addition of CO or syngas (PCO = 31.4 kPa), the metabolism of the mixed culture switched to ethanol production, at neutral pH, after increasing the reduction potential of the medium through continuous CO supply in a batch reactor. These results provide useful insights towards the sustainable production of acetate, ethanol, and other products from syngas, particularly when the composition of syngas varies depending on the type of feedstock gasified and the gasification conditions.
- CO2 :
- H2 :
- PCO :
CO partial pressure
- PCO2 :
CO2 partial pressure
- PH2 :
H2 partial pressure
chemical oxygen demand
quantitative real-time polymerase chain reaction
Vega JL, Antorrena GM, Clausen EC, Gaddy JL. Study of gaseous substrate fermenations: carbon monoxide conversion to acetate. 2. Continuous culture. Biotechnol Bioeng. 1989;34:785–93.
Vega JL, Prieto S, Elmore BB, Clausen EC, Gladdy JL. The biological production of ethanol from synthesis gas. Appl Biochem Biotechnol. 1989;20–21:781–97.
Grethlein AJ, Worden RM, Jain MK, Datta R. Evidence for production of n-butanol from carbon monoxide by Butyribacterium methylotrophicum. J Ferment Bioeng. 1991;72:58–60.
Luo G, Wang W, Angelidaki I. Anaerobic digestion for simultaneous sewage sludge treatment and CO biomethanation: process performance and microbial ecology. Environ Sci Technol. 2013;47:10685–93.
Shen Y, Brown R, Wen Z. Enhancing mass transfer and ethanol production in syngas fermentation of Clostridium carboxidivorans P7 through a monolithic biofilm reactor. Appl Energy. 2014;136:68–76.
Younesi H, Najafpour G, Mohamed AR. Ethanol and acetate production from synthesis gas via fermentation processes using anaerobic bacterium, Clostridium ljungdahlii. Biochem Eng J. 2005;27:110–9.
Rajagopalan S, Datar RP, Lewis RS. Formation of ethanol from carbon monoxide via a new microbial catalyst. Biomass Bioenerg. 2002;23:487–93.
Chen J, Henson MA. In silico metabolic engineering of Clostridium ljungdahlii for synthesis gas fermentation. Metab Eng. 2016;38:389–400.
Shen Y, Brown RC, Wen Z. Syngas fermentation by Clostridium carboxidivorans P7 in a horizontal rotating packed bed biofilm reactor with enhanced ethanol production. Appl Energy. 2017;187:585–94.
Ramió-Pujol S, Ganigué R, Baneras L, Colprim J. How can alcohol production be improved in carboxydotrophic clostridia. Process Biochem. 2015;50:1047–55.
Diender M, Stams AJM, Sousa DZ. Pathways and bioenergetics of anaerobic carbon monoxide fermentation. Front Microbiol. 2015;6:1275.
Chang IS, Kim BH, Kim DH, Lovitt RW, Sung HC. Formulation of defined media for carbon monoxide fermentation by Eubacterium limosum KIST612 and the growth characteristics of the bacterium. J Biosci Bioeng. 1999;88:682–5.
Abubackar HN, Veiga MC, Kennes C. Biological conversion of carbon monoxide: rich syngas or waste gases to bioethanol. Biofuels, Bioprod. Biorefining. 2011;5:93–114.
Abrini J, Naveau H, Nyns E-J. Clostridium autoethanogenum sp. nov., an anerobic bacterium that produces ethanol from carbon monoxide. Arch Microbiol. 1994;161:345–51.
Mohammadi M, Younesi H, Najafpour G, Mohamed AR. Sustainable ethanol fermentation from synthesis gas by Clostridium ljungdahlii in a continuous stirred tank bioreactor. J Chem Technol Biotechnol. 2012;87:837–43.
Bredwell M, Srivastava P, Worden R. Reactor design issues for synthesis-gas fermentations. Biotechnol Prog. 1999;15:834–44.
Park S, Yasin M, Kim D, Park H-D, Kang CM, Kim DJ, et al. Rapid enrichment of (homo)acetogenic consortia from animal feces using a high mass-transfer gas-lift reactor fed with syngas. J Ind Microbiol Biotechnol. 2013;40:995–1003.
Latif H, Zeidan AA, Nielsen AT, Zengler K. Trash to treasure: production of biofuels and commodity chemicals via syngas fermenting microorganisms. Curr Opin Biotechnol. 2014;27:79–87.
Bridgwater AV. The technical and economic feasibility of biomass gasification for power generation. 1995;14:631–53.
Ciferno JP, Marano JJ. Benchmarking biomass gasification technologies for fuels, chemicals and hydrogen production. US Dep Energy Natl Energy; 2002.
Diender M, Stams AJM, Sousa DZ. Production of medium-chain fatty acids and higher alcohols by a synthetic co-culture grown on carbon monoxide or syngas. Biotechnol Biofuels. 2016;9:82.
Hu P, Rismani-Yazdi H, Stephanopoulos G. Anaerobic CO2 fixation by the acetogenic bacterium Moorella thermoacetica. Am Inst Chem Eng. 2013;59:3176–83.
Sim JH, Kamaruddin AH, Long WS. Biocatalytic conversion of CO to acetic acid by Clostridium aceticum—medium optimization using response surface methodology (RSM). Biochem Eng J. 2008;40:337–47.
Ukpong MN, Atiyeh HK, De Lorme MJM, Liu K, Zhu X, Tanner RS, et al. Physiological response of Clostridium carboxidivorans during conversion of synthesis gas to solvents in a gas-fed bioreactor. Biotechnol Bioeng. 2012;109:2720–8.
Hurst KM, Lewis RS. Carbon monoxide partial pressure effects on the metabolic process of syngas fermentation. Biochem Eng J. 2010;48:159–65.
Sharak Genthner B, Bryant M. Growth of Eubacterium limosum with carbon monoxide as the energy source. Appl Environ Micriobiol. 1982;43:70–4.
Nam CW, Jung KA, Park JM. Biological carbon monoxide conversion to acetate production by mixed culture. Bioresour Technol. 2016;211:478–85.
Heiskanen H, Virkajärvi I, Viikari L. The effect of syngas composition on the growth and product formation of Butyribacterium methylotrophicum. Enzyme Microb Technol. 2007;41:362–7.
Maness P-C, Weaver PF. Production of poly-3-hydroxyalkanoates from CO and H2 by a novel photosynthetic bacterium. Appl Biochem Biotechnol. 1994;45–46:395–406.
Diender M, Pereira R, Wessels HJCT, Stams AJM, Sousa DZ. Proteomic analysis of the hydrogen and carbon monoxide metabolism of Methanothermobacter marburgensis. Front Microbiol. 2016;7:1049.
Weghoff MC, Müller V. CO Metabolism in the thermophilic acetogen Thermoanaerobacter kivui. Appl Environ Micriobiol. 2016;82:2312–9.
Drake HL. Demonstration of hydrogenase in extracts of the homoacetate-fermenting bacterium Clostridium thermoaceticum. J Bacteriol. 1982;150:702–9.
Marshall CW, LaBelle EV, May HD. Production of fuels and chemicals from waste by microbiomes. Curr Opin Biotechnol. 2013;24:391–7.
Alves JI, Stams AJM, Plugge CM, Alves MM, Sousa DZ, Madalena Alves M, et al. Enrichment of anaerobic syngas-converting bacteria from thermophilic bioreactor sludge. FEMS Microbiol Ecol. 2013;86:590–7.
Ganigue R, Ramio-Pujol S, Sanchez P, Baneras L, Colprim J, Bañeras L, et al. Conversion of sewage sludge to commodity chemicals via syngas fermentation. Water Sci Technol. 2015;72:415–20.
Pakshirajan K, Mal J. Biohydrogen production using native carbon monoxide converting anaerobic microbial consortium predominantly Petrobacter sp. Int J Hydrogen Energy. 2013;38:16020–8.
Esquivel-Elizondo S, Delgado AG, Krajmalnik-Brown R. Evolution of microbial communities growing with carbon monoxide, hydrogen, and carbon dioxide. FEMS Microbiol Ecol. 2017;93:1–12.
Miceli JF, Garcia-Peña I, Parameswaran P, Torres CI, Krajmalnik-Brown R. Combining microbial cultures for efficient production of electricity from butyrate in a microbial electrochemical cell. Bioresour Technol. 2014;169:169–74.
Delgado AG, Parameswaran P, Fajardo-Williams D, Halden RU, Krajmalnik-Brown R. Role of bicarbonate as a pH buffer and electron sink in microbial dechlorination of chloroethenes. Microb Cell Fact. 2012;11:128.
Esquivel-Elizondo S, Parameswaran P, Delgado AG, Maldonado J, Rittmann BE, Krajmalnik-Brown R. Archaea and Bacteria acclimate to high total ammonia in a methanogenic reactor treating swine waste. Archaea. 2016;2016:10.
Ritalahti KM, Amos BK, Sung Y, Wu Q, Koenigsberg SS, Löffler FE. Quantitative PCR targeting 16S rRNA and reductive dehalogenase genes simultaneously monitors multiple Dehalococcoides strains. Appl Environ Microbiol. 2006;72:2765–74.
Caporaso JG, Lauber CL, Walters WA, Berg-Lyons D, Huntley J, Fierer N, et al. Ultra-high-throughput microbial community analysis on the Illumina HiSeq and MiSeq platforms. ISME J. 2012;6:1621–4.
Masella AP, Bartram AK, Truszkowski JM, Brown DG, Neufeld JD. PANDAseq: paired-end assembler for illumina sequences. BMC Bioinform. 2012;13(1):31.
Caporaso JG, Kuczynski J, Stombaugh J, Bittinger K, Bushman FD, Costello EK, et al. QIIME allows analysis of high-throughput community sequencing data. Nat Methods. 2010;7:335–6.
Ziv-El M, Popat SC, Parameswaran P, Kang DW, Polasko A, Halden RU, et al. Using electron balances and molecular techniques to assess trichoroethene-induced shifts to a dechlorinating microbial community. Biotechnol Bioeng. 2012;109:2230–9.
Rittmann BE, McCarty PL. Environmental biotechnology: principles and applications. Boston: Mc Graw Hill; 2001.
Kim D, Chang IS. Electricity generation from synthesis gas by microbial processes: CO fermentation and microbial fuel cell technology. Bioresour Technol. 2009;100:4527–30.
Menon S, Ragsdale SW. Unleashing hydrogenase activity in carbon monoxide dehydrogenase/acetyl-CoA synthase and pyruvate: ferredoxin oxidoreductase. Biochemistry. 1996;35:15814–21.
Bertsch J, Müller V. CO metabolism in the acetogen Acetobacterium woodii. Appl Environ Microbiol. 2015;81:5949–56.
Richter H, Molitor B, Wei H, Chen W, Aristilde L, Angenent LT. Ethanol production in syngas-fermenting Clostridium ljungdahlii is controlled by thermodynamics rather than by enzyme expression. Energy Environ Sci. 2016;9:2392–9.
Liu K, Atiyeh HK, Stevenson BS, Tanner RS, Wilkins MR, Huhnke RL. Continuous syngas fermentation for the production of ethanol, n-propanol and n-butanol. Bioresour Technol. 2014;151:69–77.
Sipma J, Lens PNL, Stams AJM, Lettinga G. Carbon monoxide conversion by anaerobic bioreactor sludges. FEMS Microbiol Ecol. 2003;44:271–7.
Abubackar HN, Veiga MC, Kennes C. Biological conversion of carbon monoxide to ethanol: effect of pH, gas pressure, reducing agent and yeast extract. Bioresour Technol. 2012;114:518–22.
Klouche N, Fardeau ML, Lascourrèges JF, Cayol JL, Hacene H, Thomas P, et al. Geosporobacter subterraneus gen. nov., sp. nov., a spore-forming bacterium isolated from a deep subsurface aquifer. Int J Syst Evol Microbiol. 2007;57:1757–61.
SEE designed the study, performed the experiments, analyzed the data, and drafted the manuscript. AGD guided the experiments and analysis of the data, and reviewed the manuscript. BER and RKB reviewed the data and the manuscript. All authors read and approved the final manuscript.
Authors thank Dr. César I. Torres for his critical review of the data presented; Dr. George Papaharalabos for setting up the batch reactor with CO supply; and Diana C. Calvo for her assistance in the selection and bundle of the diffusive membranes.
The authors declare that they have no competing interests.
Availability of data and materials
The datasets generated and/or analyzed during the present study are included in this published article and are available from SEE and RKB on reasonable request. Assembled 16S rRNA sequences of the isolates are available online (https://www.ncbi.nlm.nih.gov) under the accession numbers GenBak KY992591 and KY992590. Raw sequencing Illumina data are available online (https://www.ncbi.nlm.nih.gov) under the Project ID PRJNA386595.
This work was supported in part by CAREER Award Number 1053939 and the Engineering Research Center program of the National Science Foundation (NSF) under NSF Cooperative Agreement Number EEC-1449501. Any opinions, findings and conclusions, or recommendations expressed in this material are those of the author(s) and do not necessarily reflect those of the NSF.
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