Literature DB >> 32691533

Electron availability in CO2 , CO and H2 mixtures constrains flux distribution, energy management and product formation in Clostridium ljungdahlii.

Maria Hermann1, Attila Teleki1, Sandra Weitz2, Alexander Niess1, Andreas Freund1, Frank R Bengelsdorf2, Ralf Takors1.   

Abstract

Acetogens such as Clostridium ljungdahlii can play a crucial role reducing the human CO2 footprint by converting industrial emissions containing CO2 , CO and H2 into valuable products such as organic acids or alcohols. The quantitative understanding of cellular metabolism is a prerequisite to exploit the bacterial endowments and to fine-tune the cells by applying metabolic engineering tools. Studying the three gas mixtures CO2  + H2 , CO and CO + CO2  + H2 (syngas) by continuously gassed batch cultivation experiments and applying flux balance analysis, we identified CO as the preferred carbon and electron source for growth and producing alcohols. However, the total yield of moles of carbon (mol-C) per electrons consumed was almost identical in all setups which underlines electron availability as the main factor influencing product formation. The Wood-Ljungdahl pathway (WLP) showed high flexibility by serving as the key NAD+ provider for CO2  + H2, whereas this function was strongly compensated by the transhydrogenase-like Nfn complex when CO was metabolized. Availability of reduced ferredoxin (Fdred ) can be considered as a key determinant of metabolic control. Oxidation of CO via carbon monoxide dehydrogenase (CODH) is the main route of Fdred formation when CO is used as substrate, whereas Fdred is mainly regenerated via the methyl branch of WLP and the Nfn complex utilizing CO2  + H2 . Consequently, doubled growth rates, highest ATP formation rates and highest amounts of reduced products (ethanol, 2,3-butanediol) were observed when CO was the sole carbon and electron source.
© 2020 The Authors. Microbial Biotechnology published by Society for Applied Microbiology and John Wiley & Sons Ltd.

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Year:  2020        PMID: 32691533      PMCID: PMC7533319          DOI: 10.1111/1751-7915.13625

Source DB:  PubMed          Journal:  Microb Biotechnol        ISSN: 1751-7915            Impact factor:   5.813


Introduction

Climate protection and sustainability are two of the greatest challenges for today’s society and for decision‐makers in politics and in industry. In this context, bacterial synthesis gas (syngas) fermentation represents a promising technology for the sustainable production of commodity chemicals and biofuels. It offers a possibility to replace fossil‐based resources while reducing the greenhouse gas carbon dioxide (CO2) and utilizing the waste gas carbon monoxide (CO) (Bengelsdorf and Dürre, 2017; Takors et al., 2018). For instance, this was already achieved by using exhaust gas of the steel industry as a carbon source (LanzaTech, 2018). Alternatively, syngas, a mixture mainly comprising CO, CO2 and hydrogen (H2), may be utilized as an inexpensive feedstock because it is derived from agricultural, industrial and municipal wastes (Bengelsdorf and Dürre, 2017; Takors et al., 2018). Syngas could be metabolized via hydrogenesis, methanogenesis or acetogenesis by a multitude of anaerobic bacteria thereby accessing a wide range of products (Latif et al., 2014; Diender et al., 2015; Takors et al., 2018). One popular representative of gas‐fermenting acetogenic bacteria is C. ljungdahlii. The strain was isolated in 1993 from chicken yard waste (Tanner et al., 1993). Characteristically, this bacterium shows a wide substrate spectrum. Beside different sugars, it can metabolize syngas autotrophically, CO solely and a mixture of CO2 and H2 to form the natural products acetate, ethanol, 2,3‐butanediol and lactate (Tanner et al., 1993; Köpke et al., 2010; Köpke et al., 2011). In addition, C. ljungdahlii is genetically accessible enabling metabolic engineering for the optimized formation of natural and non‐natural products (Molitor et al., 2017; Woolston et al., 2018; Huang et al., 2019). As a prerequisite of further strain application, it is crucial to understand energy and redox management in acetogens, as they are known to live at the thermodynamic edge of life (Schuchmann and Müller, 2014). C. ljungdahlii uses the WLP for the fixation of CO2 and CO (Köpke et al., 2010). The pathway consists of two branches and is characterized by the stepwise reduction of CO2 to a methyl group that is combined with CO and CoA to generate acetyl‐CoA, consuming one ATP. The conversion of acetyl‐CoA to acetate provides C. ljungdahlii one possibility to gain one ATP via substrate‐level phosphorylation (Drake et al., 2008; Ragsdale, 2008; Schuchmann and Müller, 2014). Consequently, no net ATP is produced via the central metabolism which is why C. ljungdahlii relies on a proton gradient coupled to an H+‐translocating ATPase to obtain additional ATP. To establish the proton gradient, the membrane ferredoxin:NAD oxidoreductase (Rnf complex) catalyses the oxidation of Fdred while transferring electrons to NAD+. For providing crucial reducing equivalents, either oxidation of CO via CODH or of H2 by a bifurcating hydrogenase (HYD) is used (Müller et al., 2008; Köpke et al., 2010; Tremblay et al., 2012; Wang et al., 2013). Reducing equivalents are not only needed to enhance ATP formation, they are electron donors for native products such as ethanol and 2,3‐butanediol, too (Köpke et al., 2010; Köpke et al., 2011). Therefore, C. ljungdahlii can regulate its ATP availability by redirecting the reducing equivalents in different by‐products (Mock et al., 2015; Richter et al., 2016; Molitor et al., 2017; Valgepea et al., 2017; Norman et al., 2019). Apparently, this links cellular energy formation, growth and by‐product formation with the electron availability in the gas mixture, the core topic of this study. We investigated growth kinetics and by‐product formation of C. ljungdahlii as a function of varying substrate compositions. Hence, bioreactor cultivations were performed installing controlled cultivation conditions in 2 l scale using the three different substrates CO, a mixture of CO2 and H2 and syngas. Intracellular carbon fluxes, redox metabolism and energy management were further characterized using flux balance analysis by coupling the experimentally observed uptake and production rates with a manually reconstructed genome‐scale metabolic model.

Results

Comparative autotrophic batch cultivation of C. ljungdahlii with different substrate conditions

Growth kinetics

To gain a better understanding of the carbon and energy metabolism of C. ljungdahlii, we compared growth, product formation and substrate uptake for different substrates (Figs 1 and 2). The respective total substrate‐to‐biomass and substrate‐to‐product yields are summarized in Table 2. Batch cultivations were performed in steadily gassed 2 l bioreactors using the compositions CO, CO + H and syngas in duplicates. Detailed gas compositions are described in the Experimental procedures section. In the presence of CO, two growth phases occurred with an exponential growth rate of µ exp = 0.06 ± 0.004 h−1 [average ± standard deviation] on CO and µ exp = 0.04 ± 0.007 h−1 on syngas during the first and lowered growth with µ exp = 0.01 ± 0.002 h−1 on CO and µ exp = 0.01 ± 0.001 h−1 on syngas during the following period. On contrary, C. ljungdahlii showed steady exponential growth with µ exp = 0.024 ± 0.003 h−1 utilizing CO2 + H2. After approximately 140 h, the maximum cell dry weight (CDW) of 0.93 ± 0.08 g l−1 and CDW = 0.76 ± 0.06 g l−1 was achieved representing 6.8 ± 0.7% and 2.7 ± 0.1% of totally captured CO and syngas respectively. The CO2 + H2 approach fixed 3.1 ± 0.1% of captured carbon as biomass reaching maximum CDW = 0.26 ± 0.001 g l−1 already after 120 h. In agreement with the growth phenotype, two phases of gas uptake were observed when CO was present. Proportional to the growth, the preferred substrate CO was consumed exponentially yielding a maximum volumetric uptake rate of 12.7 ± 0.4 mmol (l h)−1, i.e. q CO = 23.8 ± 1.3 mmol (g h)−1, both in the CO and the syngas approach. CO uptake was accompanied by a proportional CO2 formation achieving a maximum formation rate of 9.6 ± 0.5 mmol (l h)−1, i.e. qCO2 = 17.9 ± 0.4 mmol (g h)−1. In the following growth phase, both volumetric rates remained almost constant. The values are in good accordance with previously described CO uptake and CO2 production rates of Clostridium autoethanogenum and C. ljungdahlii cultivated on syngas in a chemostat mode with a dilution rate of 0.04 h−1. The authors determined CO uptake rates of 18.4–30 mmol (g h)−1 and CO2 formation rates of 4–20 mmol (g h)−1 with different biomass concentrations and H2 proportions in the substrate gas cultivating C. autoethanogenum. For C. ljungdahlii, CO uptake rates of 16.6–32.7 mmol (l h)−1 and CO2 production rates of 2.1–16.6 mmol (l h)−1 were reported (Richter et al., 2013; Martin et al., 2016; Valgepea et al., 2017; Valgepea et al., 2018). Remarkably, only a low mean H2 uptake of 0.29 ± 0.05 mmol (l h)−1 was observed in our syngas studies during the first growth period which even turned into H2 formation of about 0.30 ± 0.06 mmol (l h)−1 in the subsequent phase, whereas a simultaneous utilization of H2 and CO is shown in several previous studies describing continuous cultivations performed in a chemostat mode (Richter et al., 2013; Martin et al., 2016; Valgepea et al., 2017; Valgepea et al., 2018). In CO2 + H2 mixtures, both substrates were taken up simultaneously during the exponential growth with the maximum H2 uptake rate of 10.35 ± 0.10 mmol (l h)−1, i.e. q H2 = 50.8 ± 0.1 mmol (g h)−1 and the maximum CO2 uptake rate of 7.16 ± 0.27 mmol (l h)−1, i.e. q CO2 = 35.0 ± 1.2 mmol (g h)−1 after about 100 h. Subsequently, a decrease of both uptake rates was observed.
Fig. 1

Comparative analysis of growth and product formation of C. ljungdahlii based on the conversion of CO, CO2 + H2 or syngas in steadily gassed batch cultivations using stirred‐tank bioreactor. For each substrate condition, two independent experiments were performed that are demonstrated by individual graphs (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm). To determine the respective growth rate, we performed regression fitting for each data set. Growth rates µ and coefficients of determination R 2 are given in the Supplementary Material (Table S1).

Fig. 2

Comparative analysis of the gas uptake of C. ljungdahlii based on the conversion of CO, CO2 + H2 or syngas in steadily gassed batch cultivations using stirred‐tank bioreactor. For each substrate condition, two independent experiments were performed that are demonstrated by individual graphs plotted against the process time and the respective CDW (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm).

Table 2

Final biomass and product yields using CO, CO2 + H2 or syngas as substrates. 2,3‐butanediol is abbreviated by 2,3‐BD. Gas compositions are described in the ‘Experimental procedures’ the section. Values indicate mean of duplicates.

SubstrateYCDW, CO/CO2, YAcetate, CO/CO2, YEthanol, CO/CO2, Y 2,3‐BD, CO/CO2, YLactate,CO/CO2, YCO2,CO/CO2,
C‐mole mole−1 C‐mole mole−1 C‐mole mole−1 C‐mole mole−1 C‐mole mole−1 C‐mole mole−1
CO0.068 ± 0.0070.020 ± 0.010.205 ± 0.0260.078 ± 0.0070.008 ± 3.5*10−5 0.667 ± 0.050
CO2 + H2 0.031 ± 0.0010.93 ± 0.0010.019 ± 2.0*10−5
Syngas0.027 ± 0.0010.007 ± 0.0040.24 ± 0.0040.11 ± 0.0260.008 ± 0.0010.714 ± 0.003
Comparative analysis of growth and product formation of C. ljungdahlii based on the conversion of CO, CO2 + H2 or syngas in steadily gassed batch cultivations using stirred‐tank bioreactor. For each substrate condition, two independent experiments were performed that are demonstrated by individual graphs (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm). To determine the respective growth rate, we performed regression fitting for each data set. Growth rates µ and coefficients of determination R 2 are given in the Supplementary Material (Table S1). Comparative analysis of the gas uptake of C. ljungdahlii based on the conversion of CO, CO2 + H2 or syngas in steadily gassed batch cultivations using stirred‐tank bioreactor. For each substrate condition, two independent experiments were performed that are demonstrated by individual graphs plotted against the process time and the respective CDW (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm).

Product formation

Depending on the carbon source, different by‐product formation patterns were observed (Table 1). Utilizing CO, acetate, ethanol, 2,3‐butanediol and lactate were produced. Ethanol formation occurred steadily, whereas acetate was only formed during exponential growth and was consumed afterwards leaving 0.68 ± 0.27 g l –1. 2,3‐butanediol production started in the second growth phase together with lactate. Final 2,3‐butanediol and lactate titres were 1.96 ± 0.14 g l−1 and 0.21 ± 0.01 g l−1 respectively. Related final substrate‐to‐product conversion yields were 0.020 ± 0.01 C‐mole moleCO −1 for acetate, 0.205 ± 0.01 C‐mole moleCO −1 for ethanol, 0.078 ± 0.007 C‐mole moleCO −1 for 2,3‐butanediol and 0.008 ± 3.5*10−5 C‐mole moleCO −1 lactate.
Table 1

Maximal growth rates of C. ljungdahlii and final by‐product concentrations using CO, CO2 + H2 or syngas. 2,3‐butanediol are abbreviated by 2,3‐BD. Gas compositions are described in the Experimental procedures section. Rates reflect exponential growth during batch cultivation in steadily gassed stirred‐tank bioreactor. Values indicated mean of duplicates.

Substrate µ max, h‐1 cCDW, g l−1 cAcetate, g l−1 cEthanol, g l−1 c2,3‐BD, g l−1 CLactate, g l−1
CO0.058 ± 0.0040.93 ± 0.080.68 ± 0.275.23 ± 0.791.96 ± 0.140.21 ± 0.01
CO2 + H2 0.024 ± 0.0030.26 ± 0.0019.02 ± 0.390.14 ± 0.01
Syngas0.043 ± 0.0070.76 ± 0.060.38 ± 0.085.91 ± 0.954.45 ± 0.640.26 ± 0.06
Maximal growth rates of C. ljungdahlii and final by‐product concentrations using CO, CO2 + H2 or syngas. 2,3‐butanediol are abbreviated by 2,3‐BD. Gas compositions are described in the Experimental procedures section. Rates reflect exponential growth during batch cultivation in steadily gassed stirred‐tank bioreactor. Values indicated mean of duplicates. By contrast, CO2 + H2 consumption mainly caused the growth‐coupled production of acetate and ethanol, the latter in the aftermath of exponential growth. Maximum titres of acetate and ethanol were observed as 9.02 ± 0.39 and 0.14 ± 0.01 g l−1 respectively. Related substrate‐to‐product conversion yields were 0.93 ± 0.001 C‐mole moleCO2 −1 for acetate and 0.02 ± 2.0*10−5C‐mole moleCO2 −1 for ethanol. No formation of 2,3‐butanediol and lactate was found. Product formation using syngas resembled the CO phenotype although acetate formation was less pronounced. The final substrate‐specific product yields were 0.007 ± 0.004 C‐mole moleCO −1 for acetate, 0.24 ± 0.004 C‐mole moleCO −1 for ethanol, 0.11 ± 0.026 C‐mole moleCO −1 for 2,3‐butanediol and 0.008 ± 0.001 C‐mole moleCO −1 for lactate. The determined total consumption and production yields were applied to formulate cellular reduction balances for each experiment (see Supplementary Material). Estimated free Gibbs reaction energies ΔG and electron‐specific total product yields are shown in Table 3. While the total product yields remained similar for each substrate condition with around 0.25 C‐mol normalized to the provided electrons, clearly, a larger proportion of electrons was drained into products utilizing CO and syngas compared to CO2 + H2. The first fixed 62–60% electrons in products, whereas the latter only achieved 50%. In addition, the highest ΔGR was calculated when CO was consumed, underpinning the advantage of preferring CO compared to CO2 + H2 during batch cultivations.
Table 3

Carbon and electron balances, Gibb’s free reaction energies and electron‐specific overall product yields during growth of C. ljungdahlii using CO, CO2 + H2 or syngas. For gas compositions, see the Experimental procedures section. Rates reflect exponential growth during batch cultivation in steadily gassed stirred‐tank bioreactor. Values indicated mean of duplicates.

SubstrateC ‐ Balance, %e ‐ Balance, %YProducts, e ,Ye (Products), e ,ΔGR, kJ
C‐mole mole−1 mole mole−1 C‐mole−1
CO103.29 ± 2.67104.54 ± 3.770.24 ± 0.030.62 ± 0.02−47.57 ± 1.17
CO2 + H2 99.97 ± 0.16106.33 ± 0.300.27 ± 0.0020.53 ± 0.001−32.30 ± 3.33
Syngas109.74 ± 2.92101.62 ± 7.160.24 ± 0.020.60 ± 0.04−38.86 ± 8.70
Moreover, intracellular ATP pools were measured and depicted in Fig. 3. For each substrate condition, the ATP levels of one independent representative run were determined in order to qualitatively compare the three substrate conditions. All courses showed reducing trends leading to similar mean values of about 0.04 µmol gCDW −1.
Fig. 3

Intracellular ATP levels during exponential growth of C. ljungdahlii based on the conversion of CO, CO2 + H2 or syngas during batch cultivations in steadily gassed stirred‐tank bioreactors (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm). ATP levels were determined for one representative experiment of each substrate condition.

Intracellular ATP levels during exponential growth of C. ljungdahlii based on the conversion of CO, CO2 + H2 or syngas during batch cultivations in steadily gassed stirred‐tank bioreactors (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm). ATP levels were determined for one representative experiment of each substrate condition.

Simulation of intracellular flux distribution for different substrates

To investigate the links between intracellular carbon distribution, redox metabolism and energy conservation of C. ljungdahlii, flux balance analysis was performed. Accordingly, we studied intracellular flux patterns during the ‘pseudo‐steady states’ of the batch cultivations. To restrict the solution space assuring that FBA results reflect real physiological state, we constrained our model with all experimentally determined rates (O’Brien et al., 2015). We have reconstructed a small‐scale stoichiometric metabolic model (rSMM) comprising 117 intracellular and 46 transport reactions thereby balancing 180 metabolites (inner degree of freedom: 12, outer degree of freedom: 22). Mean values of the uptake and secretion fluxes for each substrate condition and growth phase detected (summarized in the Supplementary material, Tables S2 and S3), served as constraints which outlines the importance of accurate measurements. Carbon balances were closed by 103.29 ± 2.67%, 99.97 ± 0.16% and 109.74 ± 2.92% using CO, CO2 + H2 and syngas respectively. In addition, it was important to validate whether the simulation quality of our modelling approach basically allows a reliable comparison of metabolic fluxes using data of the three different substrate conditions we tested. This quality was checked by plotting simulated growth rates µ sim versus experimental observations µ exp (Fig. 4) applying growth maximization as objective function. High correlation coefficients R2>=0.9944 indicated satisfying quality of the simulated results.
Fig. 4

Simulated versus measured growth rates of C. ljungdahlii converting CO (), CO2 + H2 () or syngas () in steadily gassed batch cultivations in stirred‐tank bioreactors. For each substrate condition, two independent experiments were performed (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm).

Simulated versus measured growth rates of C. ljungdahlii converting CO (), CO2 + H2 () or syngas () in steadily gassed batch cultivations in stirred‐tank bioreactors. For each substrate condition, two independent experiments were performed (T = 37 °C; pH = 5.9; V R = 3 l; 500 rpm). Intracellular metabolic flux distributions of each growth phase are given in Figs 5, 6, 7. To assess the variability of the model calculation, FBA for each cultivation was performed. The results are demonstrated in the Supplementary Material (flux simulations). In addition, a condensed figure showing the fluxes of reducing equivalents and ATP formation normalized to the uptake rate of the respective energy source can be found in the Supplementary Material (Fig. S1). In case of sole CO use, the gas served as carbon and energy (electron) source. Remarkably, about 83% of consumed CO was converted intracellularly to CO2 thereby stoichiometrically producing Fdred via CODH. 78% of the produced CO2 left the cell which equals 61% of total CO consumed. Accordingly, the function of electron capturing dominated as 83% of CO was capitalized for Fdred formation and only 39% were captured inside serving as carbon source.
Fig. 5

Metabolic flux distributions of C. ljungdahlii based on the conversion of CO in steadily gassed batch cultivations in stirred‐tank bioreactors, performed in duplicates. Illustrated are the simulated fluxes in mmol (gCDW*h)−1 for the first () and second () growth phase.

Fig. 6

Metabolic flux distributions of C. ljungdahlii based on the conversion of CO2 + H2 in steadily gassed batch cultivations in stirred‐tank bioreactors, performed in duplicates. Illustrated are the simulated fluxes in mmol (gCDW*h)‐1 for the exponential growth phase.

Fig. 7

Metabolic flux distributions of C. ljungdahlii based on the conversion of syngas in steadily gassed batch cultivations in stirred‐tank bioreactors, performed in duplicates. Illustrated are the simulated fluxes in mmol (gCDW*h)−1 for the first () and second () growth phase.

Metabolic flux distributions of C. ljungdahlii based on the conversion of CO in steadily gassed batch cultivations in stirred‐tank bioreactors, performed in duplicates. Illustrated are the simulated fluxes in mmol (gCDW*h)−1 for the first () and second () growth phase. Metabolic flux distributions of C. ljungdahlii based on the conversion of CO2 + H2 in steadily gassed batch cultivations in stirred‐tank bioreactors, performed in duplicates. Illustrated are the simulated fluxes in mmol (gCDW*h)‐1 for the exponential growth phase. Metabolic flux distributions of C. ljungdahlii based on the conversion of syngas in steadily gassed batch cultivations in stirred‐tank bioreactors, performed in duplicates. Illustrated are the simulated fluxes in mmol (gCDW*h)−1 for the first () and second () growth phase. The provision of Fdred is the key determinant for the autotrophic metabolism of C. ljungdhalii, as it couples ATP synthesis to growth and product formation. First, Fdred is required for reducing NAD+ to NADH via the Rnf complex and NADP+ to NADPH via the Nfn complex (Wang et al., 2013; Mock et al., 2015). In turn, cells need NADH and NADPH to reduce CO2 to acetyl‐CoA in the methyl branch of WLP, the latter serving as main precursor for growth and product formation in C. ljungdahlii (Köpke et al., 2010; Köpke et al., 2011). In addition, ATP synthesis is coupled to the Rnf complex. Accordingly, the cellular energy management of C. ljungdahlii represents a concerted interplay of Nfn and Rnf complex, the CODH reaction, growth and product formation. Sixty‐one percent of consumed CO were converted to CO2 during the first exponential growth phase. The ratio of the product rates was 0.075: 1: 0.15: 0.01 for acetate, ethanol, 2,3‐butanediol and lactate resulting in the ATP yield of 0.34 mole mole(CO) −1 and the formation yields of 0.77 mole mole(CO) −1 for Fdred, 0.49 mole mole(CO) −1 for NAD+ and 0.02 mole mole(CO+H2) −1 for NADPH (Table 4). In the subsequent growth phase, the portion of Fdred formation from CO uptake almost remained similar. In addition, the produced acetate was incorporated again which lead to product formation ratios of 1: 0.2: 0.02 for ethanol, 2,3 butanediol and lactate respectively.
Table 4

ATP, Fdred and NAD+ yields derived from flux balance analysis considering exponentially growing C. ljungdahlii using CO, CO2 + H2 or syngas as substrates. The illustrated ATP yields refer to the ATPase activity coupled to the Rnf complex.

SubstrateATP, mole mole(CO+H2) −1 Fdred, mole mole(CO+H2) −1 NAD+, mole mole(CO+H2) −1 NADPH, mole mole(CO+H2) −1
CO0.340.770.490.02
CO2 + H2 0.240.440.430.008
Syngas0.320.720.470.014
In case of CO2 + H2 consumption, the formation of Fdred is ensured by the HYD reaction that is accompanied by the regeneration of NADP+ to NADPH (Schuchmann and Müller, 2012; Buckel and Thauer, 2013; Wang et al., 2013). Additionally, the Nfn reaction is needed to refill the NADP+ pool. Remarkably, the Nfn encoded transhydrogenase runs opposite to the CO case, i.e. NADPH is oxidized creating NADP+ and NADH. By taking up the substrate gases H2 and CO2 with a ratio of 2:1, C. ljungdahlii can balance the energy and redox metabolism simply by producing acetate. Thereby ATP was formed with the yield of 0.24 mole mole(H2) −1 and the formation yields of 0.44 mole mole(H2) −1 for Fdred, 0.43 mole mole(H2) −1 for NAD+ and 0.008 mole mole(H2) −1 for NADPH were achieved. Utilizing syngas C. ljungdahlii makes use of the CODH and the HYD reaction to generate Fdred. However, oxidation of H2 crucially relies on the availability of NADP+. The latter is solely provided by the formate dehydrogenase reaction of the WLP and the 2,3‐butanediol dehydrogenase. In parallel, Nfn and Rnf complexes are used to regenerate the redox metabolites oxidized ferredoxin (Fdox), NADH and NADPH. Growing on syngas 64% of CO is converted to CO2 during the first exponential growth phase when the by‐product ratios were 0.4: 1: 0.15: 0.03 for acetate, ethanol, 2,3‐butanediol and lactate respectively. The ATP yield of 0.32 mole mole(CO+H2) −1 was achieved with the formation yields of 0.72 mole mole(CO+H2) −1 for Fdred, 0.47 mole mole(CO+H2) −1 for NAD+ and 0.014 mole mole(CO+H2) −1 for NADPH. In the second growth phase, the HYD direction changed. Acetate was taken up, and the proportion of CO converted to CO2 increased to 74%. This led to a product formation rate ratio of 1: 0.18: 0.02 for ethanol, 2,3‐butanediol and lactate. Summarizing, the consumption of CO enabled highest Fdred, ATP and NADPH formation yields with respect to the electrons provided (see Table 4). Furthermore, the formation of reduced by‐products was highest, too (see Table 1).

Discussion

Growth phenotypes

During autotrophic cultivations, the composition of energy and carbon sources severely influences the growth phenotype and the product spectrum of C. ljungdahlii. Our results outline that CO consumption enabled faster growth rates than using gas mixtures of CO2 + H2. During the first period, growth rates of CO cultures with µ exp = 0.06 ± 0.004 h−1 more than doubled the rates of CO2 + H2 with µ exp = 0.024 ± 0.003 h−1 and were even faster than syngas tests characterized by µ exp = 0.04 ± 0.007 h−1. The observation reflects that putative CO‐growth inhibition, as outlined by Mohammadi et al. (2014), was not active. Apparently, dissolved CO levels were lower than the half‐saturation constant K S of 6.33 mmol l−1 and the inhibition constant K I of 4.44 mmol l‐1 identified by Mohammadi et al. (2014). Furthermore, CDW values were almost four times higher. The findings are comparable to the observation of Mayer and Weuster‐Botz (2017). They showed that Clostridium aceticum yielded almost doubled exponential growth rate and higher CDW concentration using CO instead of CO2 + H2. By analogy, C. ljungdahlii prefers CO because 0.34 mole ATP per mole CO were generated and 7% of captured carbon was used for biomass formation and maintenance needs. On contrary, only 3% of the captured carbon were fixed in biomass and only 0.24 mole ATP per mole H2 were gained when utilizing CO2 + H2. Furthermore, rising acetate concentrations are known to inhibit growth yielding higher cellular maintenance costs by decoupling proton import and ATP synthesis (Jones and Woods, 1986; Valgepea et al., 2017). As less ATP is available, utilizing CO2 + H2 cells are likely to run in ATP shortage (Valgepea et al., 2017) finally causing growth collapse. Noteworthy, the final acetate concentration of 9.02 ± 0.39 g l‐1 reached with the CO2 + H2 approach is close to the inhibitory concentration of 12 g l−1 postulated by Yang and Tsao (1994) for Clostridium acetobutylicum.

The link between ATP formation and redox balance

The findings anticipate that the consumption of CO led to a higher energy availability than the use of H2 as electron source, as already described before (Jack et al., 2019). In agreement with this hypothesis, highest ΔGR was calculated when CO was consumed compared to the substrate CO2 + H2. Interestingly, the intracellular biomass‐specific ATP pools did not differ, indicating that C. ljungdahlii is able to balance its energy requirement via a tight link between the energy and redox metabolism. A similar characteristic was also postulated for C. autoethanogenum before (Marcellin et al., 2016). Under balanced growth conditions, formate activation requires ATP which is equilibrated by the formation of acetate. Theoretically, ATP can be further generated via oxaloacetate decarboxylation, but this reaction plays only a minor role. Most important, autotrophic ATP production relies on the ATPase activity coupled to the Rnf complex. The respiratory enzyme utilizes Fdred in order to reduce NAD+ irrespective of the carbon and electron source used (Müller et al., 2008; Tremblay et al., 2012). However, the formation of Fdred is dependent on the electron source and differs for CO and H2. In case of CO, CODH is applied predominately, whereas the HYD reaction is the key for generating Fdred from H2. In addition, Fdred is needed to reduce NADP+ to NADPH. The latter greatly influences growth and the by‐product spectrum, as acetogens crucially need to balance NADPH formation with anabolic consumption (Fuhrer and Sauer, 2009). Accordingly, Fdred may be regarded as the key player providing electrons for proper distribution in ATP and products. Besides, the product spectrum has also an important influence on the efficiency of intracellular ATP availability. With increasing acetate formation during growth, the cellular ATP maintenance costs are likely to increase caused by the decoupling of the proton motive force and ATP synthesis (Jones and Woods, 1986; Valgepea et al., 2017). The trend of falling intracellular ATP levels consuming CO2 + H2 (Fig. 3) may reflect the hypothesis. However, even CO consuming cells show similar ATP decline although they may counteract the inhibitory effect of acetate by producing ethanol. Noteworthy, the latter is chaotropic which may cause additional stress per se (Valgepea et al., 2017). Schatschneider et al. (2018) determined intracellular ATP concentration of 0.095 µM gCDW −1 in C. autoethanogenum grown on CO in continuous culture. The value fits well to ATP levels determined in our study. Nevertheless, intracellular ATP levels for heterotrophically cultivated Clostridium beijerinckii and Clostridium acetobutylicum are higher by 1–2 orders of magnitude (0.55–5.1 µmol gCDW −1; Meyer and Papoutsakis, 1989; Liu et al., 2016). Apparently, this reflects the way of better ATP supply consuming sugars.

Fdred formation using different gases

The flux balance analysis revealed that with CO the provision of Fdred was ensured by the CODH reaction leading to the stoichiometric regeneration of NAD+ to NADH via the Rnf complex. Driven by the H+ export via the Rnf complex, ATP was formed while importing H+ (Tremblay et al., 2012). Concomitantly, NADPH was produced via the Nfn complex, driven by NADH formed via the Rnf complex (Mock et al., 2015). These findings reflect well the results summarized for C. autoethanogenum by Norman et al. (2019). Balancing the regeneration of reducing equivalents via the WLP 0.77 mole Fdred, 0.49 mole NAD+ and 0.02 mole NADPH per mole CO was net provided. In essence, these values represent the reducing power and energy equivalents for serving maintenance needs, cellular growth and product formation. Using CO2 + H2 as substrate, Fdred was formed by the HYD reaction that is accompanied by the regeneration of NADP+ to NADPH. To refill the high need of NADP+, the Nfn complex runs opposite to the CO case by oxidizing NADPH transferring electrons to NAD+. The latter was fuelled from the conversion of CO2 to acetyl‐CoA via the WLP. Summarizing, 0.44 mole Fdred, 0.43 mole NAD+ and 0.008 mole NADPH per mole H2 were net provided balancing the Nfn complex, the HYD reaction and the WLP. Obviously, the use of CO2 + H2 provides fewer reducing equivalents and ATP than the consumption of CO. These results show the importance of the methyl branch of WLP strongly depended on substrate and electron needs thereby shifting the main purpose: Consuming CO, the branch mainly served as acetyl‐CoA provider and contributed less to Fdred and NAD+ formation. The latter was mainly provided by the Nfn complex. In particular, only 8.7% of Fdred and 56.0% of NAD+ were drained from the methyl branch (Table 5). On contrast, when H2 + CO2 was used, the methyl branch supported Fdred formation by 16.5% and gained more importance as NAD+ provider: The total NAD+ formation relied on this source which clearly illustrates the dual function of the pathway that adapts to current substrate conditions.
Table 5

Percentage provision of NAD+ and Fdred and consumption of NADH and NADPH in the methyl branch derived from flux balance analysis considering exponentially growing cells of C. ljungdahlii using CO, CO2 + H2 or syngas as substrates.

SubstrateNAD+, %Fdred, %NADH, %NADPH, %
CO56.108.6656.1092.16
CO2/H2 10016.5410074.16
Syngas62.709.9562.7095.09
When syngas was used, the CO and CO2 + H2 scenarios somehow overlapped. The activity of the methyl branch was less than the CO2 + H2 metabolism but higher compared to the CO‐only case. This was due to the combined provision of Fdred by HYD and CODH yielding more reducing power for the reduction of CO2. Increasing fluxes through WLP with increased H2 supply were also observed by Valgepea et al. (2018) investigating continuously cultivated C. autoethanogenum on syngas. They predicted direct reduction of CO2 with H2 to formate by formateH2 lyase enabling high methyl branch activity with less redox consumption. However, said reaction is not considered in our model, as the C. ljungdahlii genome lacks the annotated gene (Köpke et al., 2010). Nevertheless, we performed additional model simulations including a formateH2 lyase for the three different substrate conditions to further assess our findings. The results are summarized in the Supplementary Material (Comparison rSMM_modified rSMM). The simulations show a partly changed flux pattern for syngas and CO2 + H2 but they support our hypotheses even more. Including formateH2 lyase activity, the methyl branch supports the Fdred formation by 39.6% on H2 + CO2 and by 20.5% on syngas. Besides, similar overlapping flux scenarios were also found for the HYD reaction, the Nfn complex and the Rnf complex. Consequently, the output of redox and energy equivalents was better than utilizing CO2 + H2 but slightly less than using CO as sole electron and substrate donor.

Product formation

The product‐per‐electron yield in mol‐C was fairly the same in all studies (about 0.25 C‐moles per electron). The observation outlines the fundamental restriction of acetogens offering a maximum product formation that is limited by electron availability (Table 2). However, the product portfolio differed depending on the carbon and electron source. To illustrate the spectrum, the electron efficiency Ye,e was calculated, i.e. the fraction of ‘free electrons’ found in the product versus consumed electrons in the substrates. Utilizing CO solely, about 62% of substrate electrons were found in the products mirroring that the reduction degree of all products was the highest when using CO. The utilization of syngas still showed the same trend but the changing flux distributions (see above) finally lowered the reduction degree of the products. When the mixture of CO2 and H2 was applied, Ye,e was found to be the lowest, again mirroring the changed intracellular flux distribution. Acetate turned out to be the dominating product when CO2 + H2 mixtures were used. The finding coincided with the complete equilibration of ATP use in the methyl branch versus ATP formation via acetate formation. The exclusive role of the methyl branch as NAD+ provider using H2 + CO2 finally lead to minimal NADH excess to produce reduced products such as ethanol. Furthermore, the ATP gain was the lowest (Table 3). When CO was applied, the methyl branch activities only halved those of H2 + CO2 and related ATP use was no longer covered by acetate formation. For compensation, NAD+ pushed the Rnf complex activity which finally provided strong ATP formation. Interestingly, the net NADH formation using CO outnumbered the needs of the low activity methyl branch which lead to the production of reduced products such as ethanol or 2,3 butanediol (Table 4). The latter represents the highest 2,3‐butanediol production of a batch process with C. ljungdahlii described so far (Köpke et al., 2011) and reflects well the hypothesis of Norman et al. (2019). They predicted high 2,3‐butandiol production under ample carbon but restricted H2 supply. Final biomass and product yields using CO, CO2 + H2 or syngas as substrates. 2,3‐butanediol is abbreviated by 2,3‐BD. Gas compositions are described in the ‘Experimental procedures’ the section. Values indicate mean of duplicates. Carbon and electron balances, Gibb’s free reaction energies and electron‐specific overall product yields during growth of C. ljungdahlii using CO, CO2 + H2 or syngas. For gas compositions, see the Experimental procedures section. Rates reflect exponential growth during batch cultivation in steadily gassed stirred‐tank bioreactor. Values indicated mean of duplicates. ATP, Fdred and NAD+ yields derived from flux balance analysis considering exponentially growing C. ljungdahlii using CO, CO2 + H2 or syngas as substrates. The illustrated ATP yields refer to the ATPase activity coupled to the Rnf complex. Percentage provision of NAD+ and Fdred and consumption of NADH and NADPH in the methyl branch derived from flux balance analysis considering exponentially growing cells of C. ljungdahlii using CO, CO2 + H2 or syngas as substrates. Summarizing, our findings confirm the hypothesis that acetogens can regulate their metabolism by coupling the redox metabolism with ATP synthesis and carbon distribution finally yielding different products (Richter et al., 2016; Valgepea et al., 2017). In this context, we identified the supply and availability of Fdred as the key determinant of metabolic control of C. ljungdahlii.

Conclusion

The metabolism of C. ljungdahlii showed high flexibility and adaption for optimum use of CO, CO2 + H2 and syngas. Clearly, the application of CO as substrate and electron donor is favoured with respect to growth rate, ATP supply and the formation of reduced products. The yield of electrons bound in products compared to electrons used in substrates is the highest for CO. This mirrors the dual role of the methyl branch of the WLP which showed comparably low activity under CO consumption thereby providing excess NADH to produce alcohols. Thereof, the conclusion could be drawn that CO should be the preferred substrate for the production of natural or even non‐natural alcohols with C. ljungdahlii. Accordingly, CO‐rich off‐gases of the steel industry should be ideal substrates for the production of alcohols (Sun et al., 2019).

Experimental procedures

Bacterial strain, growth medium and preculture preparation

C. ljungdahlii (DSM 13528) was obtained from the German Collection of Microorganisms and Cell Culture (DSMZ). All experiments were performed under strict anaerobic conditions (Hungate, 1969) using the Tanner mod. PETC medium (ATCC medium 1754) with 15 g l−1 MES buffer and 0.5 g l−1 yeast extract (Tanner et al., 1993). The redox indicator resazurin was solely used for the preculture steps prior to the controlled cultivation in the bioreactor. The preculture seed train contained heterotrophic as well as autotrophic cultivation steps. A frozen cell stock was used to inoculate 5 ml of a heterotrophic medium with 10 g l−1 fructose in an unshaken 10 ml anaerobic hungate tube (Glasgerätebau Ochs, Bovenden/Lenglern, Germany) which was incubated for 48 h at 37 °C. Next, 4% (vv−1) cell suspension of the preculture was transferred into 50 ml of a heterotrophic medium with 10 g l−1 fructose into an anaerobic cultivation bottle with total a volume of 100 ml (Duran protect, Duran group GmbH, Mainz, Germany). The culture was incubated for 48 h at 37 °C and 100 rpm on an orbital shaker (New Brunswick Scientific, Connecticut, USA). In order to adapt the cells to the fructose‐free medium in the bioreactor, an additional preculture step was performed comprising anaerobic cultivation in 500 ml bottles filled with 100 ml fructose‐free medium. Before inoculating the medium with 4 ml preculture, the headspace of the bottles was exchanged three times with the filter‐sterilized gas mixture. Then, 2 bar overpressure was installed and the culture was incubated at 37 °C and 100 rpm. Exponentially growing cells of this seed step were used to inoculate the bioreactor.

Batch cultivation studies in a stirred‐tank reactor with different substrates

Anaerobic autotrophic batch cultivations with different substrate gas compositions were performed in a fully controlled 3 l stirred‐tank bioreactor (Bioengineering, Wald, Switzerland) with an operational volume of 1.5 l. The bioreactor was equipped with sensors for pH (Mettler Toledo, Columbus, OH, USA), redox potential (Mettler Toledo, Columbus, OH, USA), pressure (Keller AG für Druckmesstechnik, Winterthur, Switzerland) and temperature. LabVieW was used to track process parameters. Temperature was set at 37 °C, and pH was kept constant at 5.9 using 2 M NaOH for titration. Four mass flow controllers (Bronkhorst High‐Tech B.V., Ruurlo, Netherlands) were used to apply different gas mixtures and flows. In the baffled bioreactor, an L‐tube sparger and a six‐blade Rushton impeller stirring with an agitation speed of 500 rpm ensured gas dispersion. The mass spectrometer (Prima Pro, Thermo Fischer Scientific, Waltham, USA) allowed the online measurement of the reactor off‐gas. To avoid foam formation during the batch processes, the antifoam Struktol 674 (Still und Seilacher) was added manually using sterile single‐use syringes and cannulas via a septum (Carl Roth GmbH + Co. KG, Karlsruhe, Germany). Three gas compositions were tested in duplicates: (i) CO (39% CO; 4% CO2; 57% Ar) with a constant gassing rate of 18.9 l h−1, (ii) CO (47.5% H2; 47.5% CO2; 5% Ar) with a constant gassing rate of 13.2 l h−1 and (iii) syngas (55% CO; 30% H2; 5% CO2; 10% Ar) with a constant gassing rate of 13.2 l h−1. As we only had a limited number of gas flow controllers (two at the beginning of our study and three at the end), we partly had to work with predefined gas mixtures. Therefore, it was not possible to establish identical gassing rates and partial pressures of the substrate components for all conditions. We assumed equal supply conditions for all tests, given that average residence time of gas was 11 s in the stirred bioreactor. The latter was estimated considering the reactor diameter and a turbulence factor for the rise velocity of bubbles (Alves et al., 2004). To ensure anaerobic conditions, the medium containing bioreactor was sparged with nitrogen with a gassing rate of 60 l h−1 applied for 2 h. Off‐gas measurements ensured that oxygen concentrations were always below 0.01% (vv−1). Afterwards, the medium was equilibrated with one of the gas compositions (i)–(iii) for 5 h. Two hours prior to inoculation of the bioreactor, sterile reducing agent was added (Tanner et al., 1993). During the cultivations, samples were taken frequently to determine the CDW, the extracellular product formation and the intracellular ATP pools.

Analytical methods

Biomass concentration analysis

The optical density was measured offline via a UV/Visible spectrophotometer (Ultrospec 1100 pro, Amersham Bioscience GmbH, Freiburg, Germany) at 600 nm. Thereof, the CDW concentration in [gCDW l−1] was correlated with CDW‐to‐OD600nm as 0.25. CDW measurements were based on twice washed (mineralized water) pellets of three 4 ml samples of the cell suspension, centrifuged at 6900 rcf and 4 °C for 5 min (5430 R, Eppendorf, Hamburg, Germany), which were transferred to preweighed glass vials with a total volume of 1.5 ml and dried at 105 °C for at least 24 h in a convection oven (Heraeus, Hanau, Germany). Empty glass vials and the cell pellets were stored in a desiccator (Duran vacuum desiccator, DWK Life Sciences GmbH, Mainz, Germany) for several hours before weighting.

Analysis of extracellular products

The detection of the by‐products ethanol, acetate, 2,3‐butanediol and lactate was carried out by an isocratic high‐performance liquid chromatography (HPLC), equipped with a RI detector (1200 Series, Agilent, Santa Clara, CA, USA) and a Rezex ROAOrganic Acid H+ column, at a temperature of 55 °C. A 5 mM H2SO4 was used as effluent with a flow rate of 0.4 ml min−1. Cell‐free samples were generated by centrifugation (5430 R, Eppendorf, Hamburg, Germany) of the cell suspension at 18 000 rcf and 4 °C for 2 min. Subsequently, samples were pretreated consecutively with 4 M NH3 and 1.2 M MgSO4 solutions to precipitate phosphate and were finally incubated with 0.1 M H2SO4.

Analysis of the intracellular ATP concentrations

Intracellular ATP pool concentrations in [µmol gCDW −1] were quantified using an HPLC system (1200 Series, Agilent, Santa Clara, CA, USA) coupled to a triple quadrupole tandem mass spectrometer (QQQ‐MS/MS) equipped with an electrospray ion source (Agilent 6410B, Agilent Technologies, Waldbronn, Germany). The method based on a bicratic zwitterionic hydrophilic interaction chromatography (ZIC‐pHILIC) with alkaline (pH 9.2) mobile phase conditions (Teleki et al., 2015). The detection was carried out in negative (ESI‐) ionization mode and multiple reaction monitoring (MRM) mode with preoptimized precursor‐to‐product ion transitions (Teleki et al., 2015). The ATP standard was obtained from Sigma‐Aldrich (Schnelldorf, Germany). MS‐grade water, methanol, chloroform and acetonitrile were purchased from Carl Roth (Karlsruhe, Germany). Standard stock solutions of ATP were prepared in MS‐grade water and stored at −70 °C. Sample preparation was based on an adapted sequential protocol via fast centrifugation treatment (FCT; Plassmeier et al., 2007) and a subsequent cold methanolchloroform extraction (CME; de Koning and van Dam, 1992). During the exponential growth phase of batch cultures, 5 ml cell suspension was taken periodically as triplicates. The samples were centrifuged at 6900 rcf and −11 °C for 2 min (5430 R, Eppendorf, Hamburg, Germany) and subsequently washed with 5 ml ice‐cold isotonic 0.9% (vv−1) sodium chloride solution. Resulting cell pellets and cultivation supernatants (analogues extracellular samples) were immediately quenched by liquid nitrogen and temporarily stored at −70 °C. Defined cell amounts were resuspended in 200 µl of a precooled 50% (vv−1) methanol solution by pulse vortexing (20 s) and merged with 200 µl of precooled chloroform. These extraction solutions were shaken for 1.5 h at −20 °C and subsequently for 1 h at room temperature using a cellmixer (CMV, Labortechnik Fröbel GmbH, Lindau, Germany). After a centrifugation step at 18 000 rcf at −11 °C for 15 min (5430 R, Eppendorf, Hamburg, Germany), the upper aqueous methanol phase (ATP extracts) was removed and temporarily stored at −70 °C. ATP concentrations were absolutely quantified by a standard‐based external calibration using isotope dilution mass spectrometry (IDMS) as quantification strategy. Prior to analysis, samples and standard mixtures were prepared by constant addition of 10 mM ammonium acetate, 60% (vv−1) acetonitrile, 2.5 mM 2‐keto‐3‐deoxy‐6‐phosphogluconate (KDPG) and 8% (vv−1) uniformly labelled (U‐13C) Corynebacterium glutamicum metabolite extracts (Feith et al., 2019). The external calibration range (2.5 nM to 40 µM) with 19 levels was adapted based on previous measurements. Calibration curves were prepared by linear regression of ratios of non‐labelled ATP peak areas and U‐13C‐labelled analogues as internal standard against the respective concentration levels. KDPG was considered for monitoring of instrumental fluctuations but not for normalization of obtained peak areas.

Online analysis of the exhaust gas

The exhaust gas was monitored online by mass spectrometry (Prima Pro, Thermo Fischer Scientific, Waltham, USA). The molar CO, CO2 and H2 concentrations produced or consumed by C. ljungdahlii in the course of the different cultivations were determined by taking into account the adjusted inlet flow rates of the individual gases as well as the measured gas concentrations in the inlet and outlet gas streams (formula 1). In each case, Argon was used as inert gas. R represents the volumetric uptake rate of the respective gas at one time point of the cultivation process. For the values of the pressure p, the temperature T and the gas constant R normal conditions are assumed. V reflects the aeration rate, and V is the working volume of the reactor. To account for dissolved CO2, total inorganic carbon in cell‐free filtrates was measured using a TC analyser (Multi N/C 2100s, Analytik Jena, Jena, Germany) as described in Graf et al. (2018). To calculate the molar concentrations of the gases produced or consumed by the cells as function of the process time, the volumetric rates were integrated.

Determination of cell specific rates

The biomass‐specific substrate uptake and product formation rates were calculated by dividing the exponential growth rate µ by the biomass substrate yield Y or the biomass product yield Y respectively (formulas 2 and 3). In prior, the exponential growth rate µ was determined graphically by a linear fit of the semilogarithmic plot of the calculated CDW as function of the process time. To deduce graphically the biomass substrate yields as well as the biomass product yields, a linear regression of the substrate or product concentration curves as function of the biomass concentration was applied. In addition, electron‐specific overall product yields were calculated (formulas 4 and 5) by assuming that one mole CO2 produced and/or one mole H2 incorporated yield two electrons that can be transferred to reducing equivalents (Müller, 2003). C represents the molar concentration of the respective product, c CO2 and c H2 are the molar concentrations of CO2 produced and H2 consumed at the end of the respective cultivation, and κ reflects the degree of reduction per carbon of the respective product.

Determination of the Gibbs free energy changes ΔGR

In order to evaluate the energy yield of the different analysed substrate conditions, the Gibbs free reaction energy change ΔG was determined as described by (Villadsen et al., 2011; formula 4) and (formula 5). ΔG is the free energy of combustion of the reactant i, that is dependent on the respective degree of reduction κ. The experimental coefficients Y and Y reflect the yields of products and substrates in mol‐C. The respective coefficients for H2O, NH3 and H+ were estimated assuming elemental balances. The biomass composition was assumed according to Alberty (1998). A detailed description is attached in the Supplementary Material.

Stoichiometric metabolic modelling

Stoichiometric network reconstruction

Based on the genome annotation of C. ljungdahlii (Köpke et al., 2010), the genome‐scale models of C. ljungdahlii (Nagarajan et al., 2013) and of the related clostridial strain C. acetobutylicum (Senger and Papoutsakis, 2008), we manually reconstructed a reduced stoichiometric metabolic model (rSMM) using the combined information from the databases KEGG and MetaCyc, literature and own experimental results. In addition, we compared our model with the metabolic model of C. autoethanogenum (Marcellin et al., 2016). The network was reconstructed, checked for consistency and topologically investigated by means of the Insilico Discovery™ platform (Insilico Biotechnology AG, Stuttgart, Germany). For the sake of simplicity, biosynthetic pathways of glycerophospholipids, cell wall, DNA and nucleotides were lumped. To cover maintenance demands, the growth‐associated value (GAM) of 46.7 mmol ATP per g CDW was installed (Nagarajan et al., 2013), whereas non‐growth‐associated maintenance (NGAM) was set to 5 mmol (gCDW*h)−1. This value corresponds to the mean maintenance cost identified for the closely related acetogen C. autoethanogenum on CO, syngas and CO2 + H2 (Valgepea et al., 2018; Heffernan et al., 2020). In addition, we made the following assumptions: (i) The ATP synthase reaction is characterized by a conservative stoichiometry of 3.66 H+ per 1 ATP (Mock et al., 2015); (ii) the HYD is an electron‐bifurcating, NADP+ and ferredoxin‐dependent enzyme that uses 2 H2 for the reversible reduction of NADP+ and Fdox (Mock et al., 2015); (iii) the formate dehydrogenase reaction is based on NADPH and Fdred as electron donor (Schuchmann and Müller, 2014); (iv) the membrane‐bound Rnf complex translocates 2 protons via the Fdred:NAD+ oxidoreductase reaction (Perez et al., 2013); and (v) the methylene‐H4F reductase reaction catalyses the reduction of methylene‐H4 presumably coupled to the reduction of ferredoxin Fdox with NADH (Köpke et al., 2010; Mock et al., 2015). Accordingly, Fdox, ATP and 2 NADH are converted to Fdred, ADP and 2 NAD+. The direct reduction of CO2 with H2 to formate by formateH2 lyase was not considered in our model, as the C. ljungdahlii genome lacks the annotated gene (Köpke et al., 2010). However, formateH2 lyase activity was identified for CO consuming C. autoethanogenum (Wang et al., 2013). Therefore, an additional model containing the aforementioned reaction (modified rSMM) was used to further assess our simulative results. Both models are attached in the Supplementary Material.

Flux balance analysis

Flux balance analysis (FBA) was performed to investigate the intracellular carbon, redox and energy balances of C. ljungdahlii as a function of varying substrate conditions (Schilling et al., 2000; Orth et al., 2010). This was necessary as the degree of freedom of the model exceeds the maximal number of quantifiable fluxes. For simulations, the Insilico Discovery™ platform was used. Maximization of biomass production was set as objective function, while all experimentally determined extracellular substrate uptake and product formation rates were used as constraints. YE was not considered for modelling, as only 0.5 g l−1 YE was provided in the batch medium accounting for < 5% of the incorporated carbon during all cultivations we described. This is reflected by well‐closed balances for measured carbon without YE consideration. Total organic carbon content in YE was measured using a TC analyser (Graf et al., 2018). We normalized the sum of the product fluxes to the sum of substrate fluxes (set to 100%) and analysed the relative distributions. Due to the reversibility of the phosphotransacetylase, the acetate kinase, aldehyde oxidoreductase and the acetaldehyde/alcohol dehydrogenase reactions, non‐realistic futile cycling may occur biasing ATP formation. To prevent non‐wanted ATP futile cycles via acetate and ethanol formation, the following constraint was additionally set: We limited the acetyl‐CoA synthase flux (r ACCOAS) by the simulated maximum using experimentally observed substrate uptake rates. Consequently, this maximum also limited the phosphotransacetylase reaction (r PTA) which, again, served as upper limit for the acetate kinase reaction (r ACK). Accordingly, a two‐step simulation was performed preventing non‐wanted futile cycling.

Conflict of interest

None declared. Fig. S1. Metabolic fluxes of reducing equivalents and ATP formation for growth of C. ljungdahlii based on the conversion of CO in the first (A) and second growth phase (B), on CO2+H2 (C) or syngas in the first (D) and second growth phase (E). The simulated rates were normalized to the respective uptake rate of the energy source (CO or H2). For each substrate condition two independent steadily gassed batch cultivations in stirred‐tank bioreactors were performed (T = 37°C; pH = 5.9; V R = 3 l; v = 500 rpm). Click here for additional data file. Table S1. Determination of the exponential growth rate for each data set and growth phase observed using regression fitting. Summarized are the determined growth rates µ and the corresponding coefficients of determination R 2 for the cultivation experiments with the three substrate gases CO (39% CO, 4% CO2, 57% Ar), CO2+H2 (47.5% H2, 47.5% CO2, 5% Ar) and syngas (55% CO, 30% H2, 5% CO2, 10% Ar) performed in duplicates. Table S2. Experimentally determination of the substrate uptake and product formation rates rate for each data set and growth phase detected. Summarized are the biomass substrate and biomass product yields Yx/s and YX/P, the corresponding coefficients of determination R2 as well as the subsequently determined substrate uptake and product formation rates for the cultivation experiments with the three substrate gases CO (39% CO, 4% CO2, 57% Ar), CO2+H2 (47.5% H2, 47.5% CO2, 5% Ar) and syngas (55% CO, 30% H2, 5% CO2, 10% Ar) performed in duplicates. Table S3. Mean values of the uptake and secretion fluxes used as constraints for FBA and the corresponding standard deviations for the cultivation experiments with the three substrate gases CO (39% CO, 4% CO2, 57% Ar), CO2+H2 (47.5% H2, 47.5% CO2, 5% Ar) and syngas (55% CO, 30% H2, 5% CO2, 10% Ar) performed in duplicates. Click here for additional data file.
  42 in total

Review 1.  Acetone-butanol fermentation revisited.

Authors:  D T Jones; D R Woods
Journal:  Microbiol Rev       Date:  1986-12

2.  Quantitative Isotope-Dilution High-Resolution-Mass-Spectrometry Analysis of Multiple Intracellular Metabolites in Clostridium autoethanogenum with Uniformly 13C-Labeled Standards Derived from Spirulina.

Authors:  Sarah Schatschneider; Salah Abdelrazig; Laudina Safo; Anne M Henstra; Thomas Millat; Dong-Hyun Kim; Klaus Winzer; Nigel P Minton; David A Barrett
Journal:  Anal Chem       Date:  2018-03-21       Impact factor: 6.986

Review 3.  Autotrophy at the thermodynamic limit of life: a model for energy conservation in acetogenic bacteria.

Authors:  Kai Schuchmann; Volker Müller
Journal:  Nat Rev Microbiol       Date:  2014-11-10       Impact factor: 60.633

4.  Rediverting carbon flux in Clostridium ljungdahlii using CRISPR interference (CRISPRi).

Authors:  Benjamin M Woolston; David F Emerson; Devin H Currie; Gregory Stephanopoulos
Journal:  Metab Eng       Date:  2018-06-15       Impact factor: 9.783

5.  Different biochemical mechanisms ensure network-wide balancing of reducing equivalents in microbial metabolism.

Authors:  Tobias Fuhrer; Uwe Sauer
Journal:  J Bacteriol       Date:  2009-01-30       Impact factor: 3.490

6.  NADP-specific electron-bifurcating [FeFe]-hydrogenase in a functional complex with formate dehydrogenase in Clostridium autoethanogenum grown on CO.

Authors:  Shuning Wang; Haiyan Huang; Jörg Kahnt; Alexander P Mueller; Michael Köpke; Rudolf K Thauer
Journal:  J Bacteriol       Date:  2013-07-26       Impact factor: 3.490

7.  Kinetic studies on fermentative production of biofuel from synthesis gas using Clostridium ljungdahlii.

Authors:  Maedeh Mohammadi; Abdul Rahman Mohamed; Ghasem D Najafpour; Habibollah Younesi; Mohamad Hekarl Uzir
Journal:  ScientificWorldJournal       Date:  2014-01-30

8.  Characterizing acetogenic metabolism using a genome-scale metabolic reconstruction of Clostridium ljungdahlii.

Authors:  Harish Nagarajan; Merve Sahin; Juan Nogales; Haythem Latif; Derek R Lovley; Ali Ebrahim; Karsten Zengler
Journal:  Microb Cell Fact       Date:  2013-11-25       Impact factor: 5.328

Review 9.  Using gas mixtures of CO, CO2 and H2 as microbial substrates: the do's and don'ts of successful technology transfer from laboratory to production scale.

Authors:  Ralf Takors; Michael Kopf; Joerg Mampel; Wilfried Bluemke; Bastian Blombach; Bernhard Eikmanns; Frank R Bengelsdorf; Dirk Weuster-Botz; Peter Dürre
Journal:  Microb Biotechnol       Date:  2018-05-14       Impact factor: 5.813

10.  Enhancing CO2-Valorization Using Clostridium autoethanogenum for Sustainable Fuel and Chemicals Production.

Authors:  James K Heffernan; Kaspar Valgepea; Renato de Souza Pinto Lemgruber; Isabella Casini; Manuel Plan; Ryan Tappel; Sean D Simpson; Michael Köpke; Lars K Nielsen; Esteban Marcellin
Journal:  Front Bioeng Biotechnol       Date:  2020-03-27
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  5 in total

1.  Metabolic engineering of Clostridium ljungdahlii for the production of hexanol and butanol from CO2 and H2.

Authors:  Ira Lauer; Gabriele Philipps; Stefan Jennewein
Journal:  Microb Cell Fact       Date:  2022-05-14       Impact factor: 6.352

Review 2.  The Potential of Sequential Fermentations in Converting C1 Substrates to Higher-Value Products.

Authors:  Christina Stark; Sini Münßinger; Frank Rosenau; Bernhard J Eikmanns; Andreas Schwentner
Journal:  Front Microbiol       Date:  2022-06-03       Impact factor: 6.064

Review 3.  Engineering Acetogenic Bacteria for Efficient One-Carbon Utilization.

Authors:  Hyeonsik Lee; Jiyun Bae; Sangrak Jin; Seulgi Kang; Byung-Kwan Cho
Journal:  Front Microbiol       Date:  2022-05-09       Impact factor: 6.064

4.  Enhanced sequestration of carbon dioxide into calcium carbonate using pressure and a carbonic anhydrase from alkaliphilic Coleofasciculus chthonoplastes.

Authors:  Jonas Heuer; Yasemin Kraus; Marijan Vučak; An-Ping Zeng
Journal:  Eng Life Sci       Date:  2021-07-26       Impact factor: 2.678

5.  Comparison of Syngas-Fermenting Clostridia in Stirred-Tank Bioreactors and the Effects of Varying Syngas Impurities.

Authors:  Luis Oliveira; Anton Rückel; Lisa Nordgauer; Patric Schlumprecht; Elina Hutter; Dirk Weuster-Botz
Journal:  Microorganisms       Date:  2022-03-22
  5 in total

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