- Open Access
Metabolic engineering of Clostridium cellulolyticum for the production of n-butanol from crystalline cellulose
Microbial Cell Factoriesvolume 15, Article number: 6 (2016)
Sustainable alternatives for the production of fuels and chemicals are needed to reduce our dependency on fossil resources and to avoid the negative impact of their excessive use on the global climate. Lignocellulosic feedstock from agricultural residues, energy crops and municipal solid waste provides an abundant and carbon-neutral alternative, but it is recalcitrant towards microbial degradation and must therefore undergo extensive pretreatment to release the monomeric sugar units used by biofuel-producing microbes. These pretreatment steps can be reduced by using microbes such as Clostridium cellulolyticum that naturally digest lignocellulose, but this limits the range of biofuels that can be produced. We therefore developed a metabolic engineering approach in C. cellulolyticum to expand its natural product spectrum and to fine tune the engineered metabolic pathways.
Here we report the metabolic engineering of C. cellulolyticum to produce n-butanol, a next-generation biofuel and important chemical feedstock, directly from crystalline cellulose. We introduced the CoA-dependent pathway for n-butanol synthesis from C. acetobutylicum and measured the expression of functional enzymes (using targeted proteomics) and the abundance of metabolic intermediates (by LC-MS/MS) to identify potential bottlenecks in the n-butanol biosynthesis pathway. We achieved yields of 40 and 120 mg/L n-butanol from cellobiose and crystalline cellulose, respectively, after cultivating the bacteria for 6 and 20 days.
The analysis of enzyme activities and key intracellular metabolites provides a robust framework to determine the metabolic flux through heterologous pathways in C. cellulolyticum, allowing further improvements by fine tuning individual steps to improve the yields of n-butanol.
Liquid transportation fuels are unsurpassed in terms of energy density and they are essential for the transport, haulage and aviation industries. Most liquid transportation fuels and many industrial chemicals are still produced from oil, a fossil resource that is becoming increasingly expensive due to the rising costs of exploration and refinery, and the geopolitical instability in some oil-producing regions. Alternative carbon-neutral energy sources are therefore required to maintain the basis of our technological society without further damage to the environment. Resources such as solar, wind, biomass and geothermal energy production are suitable for static consumers such as homes and workplaces but their conversion to liquid fuels is expensive . Because liquid fuels and green chemicals are necessary for transport and as feedstock for the chemicals industry, there is a tremendous need for the conversion of biomass into green chemicals.
Current biofuel production relies heavily on crops such as maize, but these are also used as food and feed resulting in competition for land and resources [2, 3]. Next-generation biofuels and green chemicals will be produced from lignocellulosic materials, such as agricultural residues, woody energy crops and municipal solid waste, which are abundant and inexpensive [3–5]. The main component of lignocellulose is cellulose, a polymer composed of glucose monomers, but the complex structures of lignocellulose and cellulose make them highly resistant to microbial digestion [6, 7]. Such materials must therefore be pretreated, e.g. by exposure to heat and/or chemicals, followed by digestion with cellulases produced by fungi such as Trichoderma reesei, before adding the bacteria or yeast that carry out fermentation (reviewed in [7–9]). These pretreatments tend to be energy-demanding and expensive, cancelling out many of the benefits of renewable energy [8, 10–12].
Several species of anaerobic bacteria can break down cellulose and hemicellulose efficiently, including those of the genera Clostridium, Ruminococcus and Thermoanaerobacterium [13–15]. These bacteria secrete multi-enzyme complexes known as cellulosomes, which convert cellulose into cellobiose and cellodextrins [14–17]. The products are then reabsorbed by the bacteria and metabolized further. One well-characterized example is the model organism is Clostridium cellulolyticum, a bacterium that can grow on crystalline cellulose [18–20] and which produces more than 90 glycoside hydrolases (GHs) from different families . The metabolic engineering of cellulose-degrading bacteria to produce specific products would reduce the need for pretreatment, which is the most costly process step , and could also reduce the number of steps required to produce biofuels and chemical precursors in a consolidated bioprocess [15, 22, 23].
Butanol is an advanced biofuel with a higher energy content but lower volatility than ethanol, allowing it to be blended with alkanes without the hygroscopicity associated with ethanol blending [5, 24, 25]. Butanol, especially the n-butanol isomer, is also an important feedstock for the synthesis of acrylate and methacrylate esters, glycol ethers, butyl acetate, butylamines and amino resins, and it is widely used as a solvent in the chemical industry [5, 24, 26]. Butanol can be produced by anaerobic fermentation using various Clostridium species including C. acetobutylicum and C. beijerincki in acetone–butanol–ethanol (ABE) fermentation processes using monomeric sugars (e.g. molasses) as a feed stock [27–29]. Butanol-producing bacteria such as C. acetobutylicum use the coenzyme A (CoA)-dependent pathway to generate n-butanol, in which two molecules of acetyl-CoA are condensed to form acetoacetyl-CoA, which is reduced over several further steps to butyryl-CoA, and finally converted to n-butanol by a bifunctional alcohol dehydrogenase. This pathway has been introduced by metabolic engineering into several heterologous bacteria, such as Escherichia coli, but the resulting n-butanol titers were much lower than in C. acetobutylicum.
Alternative non-natural pathways involving 2-ketoacid intermediates have also been introduced into E. coli, to produce either isobutanol (valine pathway)  or n-butanol (threonine pathway) . Other organisms have been engineered with these pathways, allowing the production of n-butanol or isobutanol from diverse substrates including glycerol, CO/CO2, syngas and cellulose (reviewed in [31, 32]). Interestingly, C. cellulolyticum can naturally produce isobutanol, but the introduction of the non-native 2-ketoacid pathway increased the overall titers to ~600 mg/L . The 2-ketoacid pathway requires NADPH as a cofactor, but cells generally produce NADH during glycolysis and must therefore produce NADPH either by the direct conversion of NADH using NADH kinase and ATP  or via an alternative route such as the pentose phosphate pathway (PPP). Converting hexoses through the PPP to pyruvate results in the net loss of carbon in the form of CO2, thus limiting the theoretical yield of butanol.
Here we report for the first time the metabolic engineering of C. cellulolyticum with the CoA-dependent pathway to produce n-butanol directly from crystalline cellulose. This pathway predominantly uses NADH as a cofactor. The production of n-butanol in this manner should not suffer carbon loss like the 2-ketoacid/PPP strategy, so the theoretical yield of butanol from hexoses should be higher when the bacterium is supplied with lignocellulosic material as a source of hexose monomers. The production of n-butanol is currently more expensive than ethanol, hence the latter is used more widely, but the ability to produce n–butanol from inexpensive lignocellulosic feedstock means that the process could become more economically feasible [25, 35].
Assembly of the CoA-depended pathway for n-butanol production
The E. coli atoB and C. acetobutylicum hbd, crt, bcd and adhE2 genes necessary for n-butanol production (Fig. 1) were cloned individually in the common E. coli expression vector pET-41(a)+ to establish a targeted proteomics strategy allowing the expression of each protein to be confirmed following the transformation of C. cellulolyticum. The E. coli atoB gene was chosen instead of C. acetobutylicum thl because it has a strong track record for the enhancement of butanol production  and it is not inhibited by free CoA [36, 37]. The genes were also assembled as a two-operon cluster, comprising a monocistronic operon containing adhE2 followed by a polycistronic operon containing atoB–hbd–crt–bcd, each under the control of the C. acetobutylicum thiolase promoter Pthl. The two-operon strategy was developed to boost the expression of the final gene in the n-butanol pathway (adhE2) thus creating a metabolic sink and driving the entire pathway towards completion. The clusters were assembled by site and ligation independent cloning (SLIC) and the final cluster was inserted into our in-house E. coli/Clostridium shuttle vector pIM to create the transformation vector pM9 (Fig. 2). The integrity of pM9 was verified by diagnostic restriction digestion and sequencing (Fig. 2). The pM9 vector was methylated with the MspI methyltransferase from Moraxella sp. ATCC 49670 (NEB) and then introduced into C. cellulolyticum by electroporation, with successful transformation confirmed by plasmid rescue. This was done to ensure that the complete plasmid was present. We noticed that large plasmids (>10 kb) do not routinely transform C. cellulolyticum although shorter derivatives are sometimes present after transformation. Because it is not possible to extract enough plasmid DNA directly from C. cellulolyticum to visualize in a restriction digest, the extracted DNA was first introduced back into E. coli and isolated from mini-cultures for the restriction digest. This plasmid rescue method is routinely necessary to check for the presence of the intact plasmid as shown in Fig. 2. Verified C. cellulolyticum pM9 transformants were then characterized in terms of gene expression, metabolic profiles, growth and product formation on cellobiose and crystalline cellulose substrates as carbon sources.
Analysis of n-butanol cluster proteins in C. cellulolyticum strain pM9 using targeted proteomics
The expression of the genes present in the n-butanol cluster was confirmed by targeted proteomics. Proteotypic peptides representing each protein (Additional file 1: Table S1) were identified in silico using Skyline . Extracts from E. coli strains expressing the individual proteins were compared to the proteotypic peptide library to identify the most abundant peptides with the highest signal-to-noise ratios. Extracts from wild-type E. coli and C. cellulolyticum were used as controls to ensure that the proteotypic peptides were not found in the endogenous proteome. The MS/MS spectrum corresponding to the proteotypic peptides for each gene in the n-butanol cluster confirmed that all the peptides could be detected simultaneously and that all five genes were expressed successfully in C. cellulolyticum strain pM9 (Additional file 2: Figure S1).
Next, we investigated the time-dependent activity of Pthl by taking samples throughout the cultivation of C. cellulolyticum pM9 up to 96 h post-inoculation, and measuring the abundance of each protein (Fig. 3). All the n-butanol pathway proteins were detected during all growth phases, and analysis of variance (ANOVA) revealed no significant change (p > 0.01) in the abundance of most proteins throughout the cultivation. The exception was Bcd, where we noted a small but significant (p < 0.01) decrease in abundance towards the end of the cultivation. The concentration of almost all the proteins therefore remained constant as biomass accumulated during growth, indicating that Pthl is constitutively active in C. cellulolyticum pM9 and that the proteins are expressed throughout the fermentation process. AtoB was the most abundant protein, followed by Crt, Bcd, AdhE2 and Hbd. It was therefore clear that the construction of a monocistronic operon did not favor the expression of AdhE2 as expected. Because both clusters were controlled by Pthl, the difference in protein expression was most likely associated with differences in translational efficiency as discussed below.
Quantification of n-butanol pathway intermediates
It is important to measure the abundance of pathway intermediates to identify rate-limiting steps, particularly when introducing a novel metabolic pathway into a heterologous host. We therefore developed an analytical method to measure all the intermediates in the n-butanol pathway simultaneously, i.e. acetyl-CoA, acetoacetyl-CoA, 3-hydroxybutyryl-CoA, crotonoyl-CoA and butyryl-CoA. We used this method to analyze C. cellulolyticum pM9 cultures during a 200-h fermentation. The profiles of acetyl-CoA and butyryl-CoA are shown in Fig. 4, whereas the other intermediates (acetoacetyl-CoA, 3-hydroxybutyryl-CoA and crotonoyl-CoA) were below the detection limit suggesting they were efficiently converted into downstream products. The possibility that the missing intermediates degraded during quenching and extraction was excluded by analyzing samples prepared in an identical manner from wild-type C. kluyveri, where all the intermediate CoA esters were detected (data not shown).
Growth and product formation on cellobiose and crystalline cellulose substrates
The growth of wild-type C. cellulolyticum and pM9 transformants was initially measured in CM3 medium containing cellobiose as the carbon source. Cellobiose is a disaccharide comprising two glucose residues linked by a β(1,4) glycosidic bond. Cellobiose is an ideal carbon source to investigate cellulose degradation because the same chemical bond is found in cellulose, but unlike crystalline cellulose it is soluble in water allowing cell growth to be measured by monitoring the turbidity of the suspension. The growth of the two C. cellulolyticum strains is compared in Additional file 3: Figure S2. The growth rates were similar in both strains, with doubling times of ~21 h for the wild-type strain and ~20 h for strain containing the pM9 vector. The expression of the n-butanol cluster therefore does not appear to generate a metabolic burden that delays growth. Interestingly, doubling times of ~7 h were reported in a variant CM3 medium containing cellobiose, with a fourfold higher concentration of MgCl2 and double the concentration of CaCl2 . This recipe promotes the formation of precipitates, which we avoided by using lower concentrations of these minerals, but nevertheless the report demonstrates that medium optimization can improve growth and therefore establish a faster bioprocess.
Next, we compared product formation by the two strains when supplied with cellobiose or crystalline cellulose. As expected, the wild-type C. cellulolyticum cultures produced ethanol and acetate as the main fermentation products rather than n-butanol. In contrast, strain pM9 produced n-butanol in addition to ethanol and acetate (Fig. 5). Importantly, strain pM9 produced more n-butanol when cultivated in the presence of crystalline cellulose rather than cellobiose as the sole carbon source (Fig. 5). This, to our knowledge, is the first time that n-butanol has been produced directly from crystalline cellulose using a single organism. We achieved titers of 40 and 120 mg/L n-butanol in cultures supplied with cellobiose and crystalline cellulose, respectively.
We attempted to increase the productivity of C. cellulolyticum pM9 cultures growing on cellobiose by increasing the concentration of the substrate, but there were no significant differences in the consumption of cellobiose in stationary-flask fermentations starting with cellobiose concentrations of 6, 15 and 26 g/L (Fig. 6). Regardless of the initial amount of cellobiose, only ~6 g/L of the substrate was consumed. This suggests that the ability to utilize cellobiose as a substrate is a rate-limiting step in the production of n-butanol.
The construction of entire heterologous pathways for metabolic engineering in non-model organisms, such as C. cellulolyticum described herein, can be challenging because the genetic toolbox available for this Gram-positive species is not as sophisticated as those available for laboratory models such as E. coli despite recent advances in this area (reviewed in [29, 40]). Nevertheless, we were able to construct and express a functional n-butanol pathway in C. cellulolyticum as confirmed by a targeted proteomics strategy designed to detect all five heterologous proteins, as well as the identification of some of the pathway intermediates and products. The targeted proteomics method will also be useful for the optimization of the engineered strain because it will allow the impact of genetic modifications (e.g. different promoters or ribosomal binding sites) to be monitored at the protein level. Such modifications are typically monitored by northern blotting, RNase protection assays, microarray analysis or quantitative RT-PCR, but these methods only reveal changes at the mRNA level. The direct quantitative analysis of proteins (e.g. by western blotting or ELISA) requires specific antibodies and is laborious and expensive to apply in a multiplex format. Our targeted proteomics strategy allows the simultaneous direct quantitation of multiple enzymes and therefore allows the impact of genetic changes on translational efficiency and protein turnover to be reported directly.
The n-butanol cluster was constructed as two operons driven by the Pthl promoter, specifically an upstream monocistronic operon containing adhE2 and a downstream polycistronic operon containing the other four genes, starting with atoB. We therefore anticipated that adhE2 and atoB would be expressed at similar levels, but this was not the case. One possible explanation is that the resulting mRNAs are translated with different efficiencies because they contain distinct ribosomal binding sites (AGGAGG for atoB and AGGAGU for adhE2). As discussed above, the targeted proteomics strategy could be used to evaluate modifications of the ribosomal binding site, 5′ untranslated region or codon usage, all of which are known to influence translational efficiency and mRNA stability [41–44] therefore greatly facilitating the further optimization of engineered C. cellulolyticum strains.
The commercial production of n-butanol using traditional ABE fermentation is carried out in China by Jilin Cathy Industries at a total cost of ~$US 2000 per ton, with most of the costs (~70 %) reflecting the use of maize as the feedstock . The optimization of the current pM9 strain is necessary because the final product titers are low. We achieved a final titer of 120 mg/L n-butanol from 12 g/L crystalline cellulose (Fig. 5) which is clearly not sufficient for the industrial production of fuels or chemicals, but it is equivalent to or better than n-butanol titers reported when feeding engineered strains with other lignocellulosic or renewable substrates. For example, yields of up to 28 mg/L have been achieved using switch grass , 25–300 mg/L using glycerol [46, 47], up to 148 mg/L using syngas  and ~400 mg/L using CO2 and light . Interestingly, C. cellulolyticum can naturally produce isobutanol under certain growth conditions, and this can be boosted to titers of 660 mg/L by incorporating the non-natural 2-ketoacid pathway . The engineered 2-ketoacid pathway uses NADPH, an anabolic cofactor that is not formed during glycolysis, whereas the CoA-dependent pathway uses NADH . Cells using the 2-ketoacid pathway must therefore convert NADH to NADPH or use the PPP as an alternative route for the production of isobutanol. In the PPP, carbon is lost due to decarboxylation, therefore limiting the theoretical yield of isobutanol. Clostridium spp. express a ferredoxin-NADP+ oxidoreductase that converts NADP+ to NADPH+H+ by oxidizing ferredoxin . Nevertheless, NADH+H+ is the primary electron accepter during glycolysis and the cell therefore needs an effective way to transfer electrons from NADH+H+ to ferredoxin and ultimately back to NADP+. This could be accomplished directly using the electron-bifurcation transhydrogenase (Nfn complex) initially identified in C. kluyveri and more recently also found in acetogenes such as C. ljungdahlii, C. autoethanogenum and Acetobacterium woodii , but not thus far in C. cellulolyticum.
As a starting point, we therefore introduced the Co-A dependent pathway into C. cellulolyticum. With further improvement of the pathway (based on information generated using our robust framework of targeted proteomics and the detection of intermediates) as well as host strain engineering (e.g. the knockout of genes producing undesirable byproducts such as lactate) it should be possible to increase n-butanol production even more. The CoA-dependent and 2-ketoacid pathways could also be combined, increasing the overall production of both butanol isomers when the engineered bacteria are presented with lignocellulosic feedstocks, because C5 sugars in the lignocellulosic material could enter the PPP directly (without carbon loss) and generate the NADPH required for the 2-ketoacid pathway.
Nevertheless, the yields we achieved are much lower than the those reported using traditional sugar-based feedstocks such as glucose, galactose and mannitol, where titers of up to 30 g/L have been reported following strain and process optimization . Host cell engineering is necessary to redirect flux towards n-butanol and reduce the production of undesirable byproducts [30, 45, 53, 54]. Targets reported in the literature, which also apply to C. cellulolyticum, include genes involved in the production of ethanol (ΔadhE), acetate (Δpta and Δack) and lactate (Δldh). Thus far, it has been possible to eliminate the production of lactate but not in C. cellulolyticum .
To our knowledge, this is the first report in which n-butanol has been produced directly from crystalline cellulose using a single engineered organism. This is an important finding because it allows the development of an inexpensive, consolidated bioprocess with fewer and milder pretreatment steps . In addition to the expense, energy consumption and environmental harm caused by pretreatment [7, 10, 55–57], such processes also tend to release inhibitors such as furan derivatives, weak carboxylic acids and phenolic compounds that interfere with downstream fermentation [7, 58]. Thus with milder pretreatment conditions the quantity of such inhibitors could be reduced and fermentation performance could be improved. Strategies to facilitate the development of consolidated bioprocess include the genetic engineering of natural cellulolytic microbes to produce desired products (as reported here) or to enable the fermentation of lignocellulosic feedstock with established production organisms . Furthermore, processes have been developed which involve synergistic combinations of bacterial strains with different roles in the breakdown and utilization of cellulose [45, 59]. This approach is challenging because the different bacteria compete with each other and it is difficult to keep the different populations in balance, whereas the use of a single engineered C. cellulolyticum strain improves the potential yield by allowing the process to be optimized for one bacterial population. However, the characteristics of the process (including the product titer and avoidance of byproducts) must be optimized to ensure the efficient conversion of biomass into fuels and chemicals. The further improvement of our strain to meet these criteria will be facilitated by our combined approach based on targeted proteomics and metabolite analysis.
Bacterial strains and plasmids
The E. coli strain NEB Express (NEB, Ipswich, MA, USA) was used for general cloning with vector pET-41a(+) (Novagen, Darmstadt, Germany). We developed a shuttle vector (pIM) for the transfer of constructs between E. coli stains and the C. cellulolyticum wild-type strain H10 (DSZM, Braunschweig, Germany) as well as vector pM9 containing the n-butanol gene clusters.
Media composition and cultivation
The E. coli strains were cultivated in lysogeny broth at 37 °C shaking at 220 rpm. The C. cellulolyticum stains were cultivated in CM3 medium, comprising 1.3 g/L (NH4)2SO4, 1.5 g/L KH2PO4, 2.9 g/L K2HPO4∙3H2O, 0.2 g/L MgCl2∙6H2O, 0.075 g/L CaCl2∙2H2O, 1.25 mg/L FeSO4∙7H2O, 1 mg/L resazurin, 2 g/L yeast extract, 0.5 g/L cysteine and either 6 g/L cellobiose or 12 g/L crystalline cellulose (Avicel PH101) as the carbon source. The pH was adjusted to 7.2 with 5 % Na2CO3 after sterilization and the medium was deoxygenated under an anaerobic atmosphere (5 % H2, 10 % CO2, 85 % N2). C. cellulolyticum was grown under anaerobic conditions at 34 °C. For the preparation of agar plates, the media described above were supplemented with 15 g/L agar.
Cloning the butanol cluster
The genes for the butanol cluster were sourced from two bacterial species: hbd, crt, bcd and adhE2 from C. acetobutylicum and atoB from E. coli. They were amplified from genomic DNA by PCR and transferred to the pET-41a(+) vector by SLIC . The same procedure was used to assemble the genes into clusters, one comprising the C. acetobutylicum thiolase promoter (Pthl) followed by atoB, hbd, crt and bcd, and the other comprising Pthl followed by adhE2. The clusters were then combined to place the adhE2 gene upstream of the others, and the entire construct was introduced into our in-house Gram+/− shuttle vector pIM at the XhoI and AleI sites. The final vector pM9 was sequenced to ensure correct assembly. A map of the vector is shown in Fig. 2.
Transformation of C. cellulolyticum
DNA was introduced into C. cellulolyticum by electroporation . Cells in the late exponential growth phase (10–50 mL, OD600 = 0.5–1) were chilled on ice for 30 min before centrifuging (4000×g for 10 min) and washing twice with ice-cold electroporation buffer (5 mM sodium phosphate buffer pH 7.4, 270 mM sucrose, 1 mM MgCl2) before resuspending in 200 µl of the same buffer. The competent cells were mixed with 1–5 µg of in vitro methylated DNA and transferred to a 0.2-mm gap cuvette (BioRad, Hercules, CA, USA) before electroporation with a BioRad Micropulser set at 1.5 kV. DNA was methylated with MspI methyltransferase (NEB) for at least 4 h according to the manufacturer’s instructions. The cells were allowed to recover in CM3 medium without antibiotics for 4–6 h before plating on medium containing 5 µg/L clarithromycin and 10 µg/L thiamphenicol. All procedures except the electroporation step were carried out under anaerobic conditions with anoxic solutions. Successful transformation was verified by plasmid rescue followed by a diagnostic restriction digest.
Fermentation products were quantified by GC/MS on a Shimadzu GCMS-QP2010S system (Shimadzu, Kyoto, Japan). The culture supernatant was diluted 1:10 in methanol containing 5.5 mM 1,3-propanediol as an internal standard. The temperature profile of the GC protocol included an initial 1-min step at 60 °C followed by a temperature gradient of 5 °C/min to 70 °C and 35 °C/min to 220 °C, and then a 2-min hold before cooling to 60 °C for the next run. Retention times and the quantification of ethanol, butanol and acetate were established using GC/MS-grade standards.
Sample preparation for targeted proteomics
Cells were harvested by centrifugation at 4000×g for 15 min at 4 °C, the supernatant was discarded and the pellet resuspended in 1 mL 50 mM ammonium bicarbonate (pH 7.8). The suspension was transferred to a 2-mL steel reaction tube, mixed with 0.5 g of 0.1-mm glass beads and shaken vigorously for 3 × 30 s on a bead beater (Biospec Products, Bartlesville, OK, USA) with intervening 1-min incubations on ice. The supernatant was clarified by centrifugation (13,000×g, 5 min, 4 °C) and the protein concentration was determined using Bradford Quick-Start Reagent (BioRad) against a bovine serum albumin standard curve. We then transferred 200 µg of total protein to ammonium bicarbonate buffer containing 0.05 % PPS silent sur-factant (Expedeon, San Diego, CA, USA), boiled the samples in a water bath for 5 min and reduced the proteins by adding 5 mM dithiothreitol and incubating at 60 °C for 30 min. The sample was alkylated using 15 mM iodoacetic acid at 25 °C for 30 min in the dark. The denatured protein was digested with sequencing-grade modified trypsin (Promega, Mannheim, Germany) at an enzyme:substrate ratio of 1:100 at 37 °C with vigorous shaking for at least 16 h. The peptide mix was desalted using 1-mL (30 mg) Chromabond HR-X cartridges (Macherey Nagel, Dueren, Germany) conditioned with 1 mL acetonitrile and 1 mL double-distilled water. After adding the sample, the cartridge resin was washed twice with 1 mL double-distilled water and the peptides were eluted by the stepwise addition of 250 µL 40:60 acetonitrile/water, 70:30 acetonitrile/water and finally 70:30 acetonitrile/1.0 % formic acid. The elution fractions were pooled and concentrated to a volume of ~50 µL using a SpeedVac (Eppendorf, Hamburg, Germany) at 45 °C. The samples were adjusted to a final volume of 100 µL with 0.1 % formic acid.
Prediction of peptide mass transitions
For each target protein, peptide mass transitions were predicted using Skyline  ignoring the first 25 amino acids and including all peptides 7–14 amino acids in length assuming the carbamidomethylation of cysteine residues. The declustering, entrance potential and collision energy parameters were calculated using Skyline for AB Sciex instruments. The sum of all dwell times for a maximum of 100 transitions in one run did not exceed 1 s/cycle to obtain at least 10 data points per signal. As a positive control for fusion protein expression, we monitored the proteotypic peptides LLLEYLEEK and IEAIPQIDK  derived from the glutathione-S-transferase (GST) protein fusion part.
Peptide analysis was carried out using a 3200 QTRAP triple-quadrupole analyzer (AB Sciex, Framingham, MA, USA) in electrospray ionization mode. Mixtures were separated by high performance liquid chromatography (HPLC) using an Agilent 1200 instrument (Agilent Technologies, Santa Clara, CA, USA) and an EC 150/2 Nucleoshell RP18, 2.7 µm column (Macherey Nagel) with solvent A (5 % acetonitrile/95 % water containing 0.1 % formic acid) and solvent B (95 % acetonitrile/5 % water containing 0.1 % formic acid). After 1 min at 0 % B the gradient was increased to 30 % B in 30 min and then to 100 % B in 5 min before an isocratic run at 100 % B for 8 min and final re-equilibration of the column (total run time, 60 min). To determine the proteotypic peptides, each GST-protein fusion was expressed and analyzed separately. The monoisotopic peptide mass in the +2 state was selected in Q1, and after fragmentation with peptide-specific collision energy in q2, the monoisotopic fragment y-ions in the +1 state were selected in Q3. The specific masses for this multiple reaction monitoring (MRM) of each proteotypic peptide are provided in Additional file 2: Figure S1. Two MRM ions were selected per proteotypic peptide for identification (Qualifier) and quantification (Quantifier).
After the selection of suitable proteotypic peptides (Additional file 2: Figure S1), heavy [13C 6 15 N2]-labeled peptides were used as internal standards (SpikeTides L™, JPT Peptide Technologies, Berlin, Germany). Heavy lysine (L) and arginine (R) labeling results in mass shifts of +8 (L) and +10 (R) atomic mass units. The corresponding transitions for internal standards were incorporated into our calculations. The absolute quantification of selected peptides was achieved using Q-Tag fusions (SpikeTides TQ™, JPT Peptide Technologies) according to the manufacturer’s recommendations. The 1 nmol stock of labeled Q-Tag fusion peptides was digested and desalted as described above for the extracted protein samples. Afterwards a dilution series was prepared and analyzed to calculate a standard curve used for absolute quantification. The specific masses for the MRM ions for these heavy (labeled) proteotypic peptides are provided in Additional file 2: Figure S1.
Intracellular metabolite analysis by LC/MS/MS
Intracellular metabolites were extracted by quenching the biomass using an acidic solvent mixture  and lysing the cells by vortexing on ice for 10 min. The lysate was clarified by centrifugation (13,000×g, 5 min, 4 °C) and the supernatant was neutralized with an equimolar volume of ammonium hydroxide before separation by HPLC on a Kinetex 2.6 µm C18 column 150 × 4.6 mm (Phenomenex, Aschaffenburg, Germany) as previously described . The metabolites were analyzed using a 3200 QTRAP triple-quadrupole MS (AB Sciex) in electrospray negative ionization mode. Metabolite references (acetyl-CoA, acetoacetyl-CoA, 3-hydroxybutyryl-CoA, crotonyl-CoA, butyryl-CoA and octanoyl-CoA) were tuned by direct infusion and a standard curve for correlation was generated with 3.125 µM as the lowest level showing a good signal-to-noise ratio. After flow injection optimization, quantitative analysis was carried out by MRM with octanoyl-CoA (50 µM) as an internal standard. The following transitions were used: acetyl-CoA, 807.962 → 408.000, 807.962 → 425.900, 807.962 → 461.000; acetoacetyl-CoA, 850.100 → 408.100, 850.100 → 418.900, 850.100 → 765.900; 3-hydroxybutyryl-CoA, 852.100 → 408.000, 852.100 → 426.000, 852.100 → 505.000; crotonyl-CoA, 834.100 → 408.000, 834.100 → 426.000, 834.100 → 487.000 butyryl-CoA, 835.962 → 408.000, 835.962 → 425.9, 835.962 → 489.000; octanoyl-CoA, 891.970 → 408.000, 891.970 → 425.900, 891.970 → 545.200.
Quantitative analysis of the carbon source in the culture supernatant was carried out using a Prominence HPLC System and refractive index detector (Shimadzu). Cellobiose, glucose and xylose were separated on a Rezex RCM Monosaccharide Ca+2 (8 %) 300 × 7.8 mm column (Phenomenex) in an isocratic run at 80 °C with double-distilled water as the solvent and a flow rate of 0.6 mL/min. Supernatant samples filtered and diluted with an equal volume of sorbitol (2 % v/v) were used as an internal standard.
Ajanovic A. Renewable fuels—a comparative assessment from economic, energetic and ecological point-of-view up to 2050 in EU-countries. Renew Energy. 2013;60:733–8.
Panoutsou C, Bauen A, Duffield J. Policy regimes and funding schemes to support investment for next-generation biofuels in the USA and the EU-27. Biofuels Bioprod Biorefin Biofpr. 2013;7:685–701.
Hill J, Nelson E, Tilman D, Polasky S, Tiffany D. Environmental, economic, and energetic costs and benefits of biodiesel and ethanol biofuels. Proc Natl Acad Sci USA. 2006;103:11206–10.
Heaton EA, Flavell RB, Mascia PN, Thomas SR, Dohleman FG, Long SP. Herbaceous energy crop development: recent progress and future prospects. Curr Opin Biotechnol. 2008;19:202–9.
Green EM. Fermentative production of butanol—the industrial perspective. Curr Opin Biotechnol. 2011;22:337–43.
Ljungdahl LG, Op den Camp HJM, Gilbert HJ, Harhangi HR, Steenbakkers PJM, Li X-L. Cellulosomes of anaerobic fungi. In: Uversky V, Kataeva IA, editors. Cellulosome. New York: Nova Science Publishers, Inc; 2006. p. 271–303.
Kumar P, Barrett DM, Delwiche MJ, Stroeve P. Methods for pretreatment of lignocellulosic biomass for efficient hydrolysis and biofuel production. Ind Eng Chem Res. 2009;48:3713–29.
Mosier N, Wyman C, Dale B, Elander R, Lee YY, Holtzapple M, Ladisch M. Features of promising technologies for pretreatment of lignocellulosic biomass. Bioresour Technol. 2005;96:673–86.
Mood SH, Golfeshan AH, Tabatabaei M, Jouzani GS, Najafi GH, Gholami M, Ardjmand M. Lignocellulosic biomass to bioethanol, a comprehensive review with a focus on pretreatment. Renew Sustain Energy Rev. 2013;27:77–93.
Yang B, Wyman CE. Pretreatment: the key to unlocking low-cost cellulosic ethanol. Biofuels Bioprod Bioref Biofpr. 2008;2:26–40.
Yoon LW, Ngoh GC, Chua ASM, Hashim MA. Comparison of ionic liquid, acid and alkali pretreatments for sugarcane bagasse enzymatic saccharification. J Chem Technol Biotechnol. 2011;86:1342–8.
Binder JB, Raines RT. Fermentable sugars by chemical hydrolysis of biomass. Proc Natl Acad Sci USA. 2010;107:4516–21.
Ahn HJ, Lynd LR. Cellulose degradation and ethanol production by thermophilic bacteria using mineral growth medium. Appl Biochem Biotechnol. 1996;57–58:599–604.
Bayer EA, Belaich JP, Shoham Y, Lamed R. The cellulosomes: multienzyme machines for degradation of plant cell wall polysaccharides. Annu Rev Microbiol. 2004;58:521–54.
Lynd LR, Weimer PJ, van Zyl WH, Pretorius IS. Microbial cellulose utilization: fundamentals and biotechnology. Microbiol Mol Biol Rev. 2002;66:506–77.
Doi RH, Kosugi A. Cellulosomes: plant-cell-wall-degrading enzyme complexes. Nat Rev Microbiol 2004;2:541–51.
Doi RH, Kosugi A, Murashima K, Tamaru Y, Han SO. Cellulosomes from mesophilic bacteria. J Bacteriol 2003;185:5907–14.
Giallo J, Gaudin C, Belaich JP. Metabolism and solubilization of cellulose by Clostridium cellulolyticum H10. Appl Environ Microbiol. 1985;49:1216–21.
Gal L, Pages S, Gaudin C, Belaich A, Reverbel-Leroy C, Tardif C, Belaich JP. Characterization of the cellulolytic complex (cellulosome) produced by Clostridium cellulolyticum. Appl Environ Microbiol. 1997;63:903–9.
Tardif C, Belaich A, Fierobe HP, Pages S, de Philip P, Belaich JP. Clostridium cellulolyticum: cellulosomes and cellulolysis. In: Uversky V, Kataeva IA, editors. Cellulosome. New York: Nova Science Publishers, Inc.; 2006. p. 231–59.
Lombard V, Golaconda Ramulu H, Drula E, Coutinho PM, Henrissat B. The carbohydrate-active enzymes database (CAZy) in 2013. Nucleic Acids Res. 2014;42:D490–5.
Olson DG, McBride JE, Shaw AJ, Lynd LR. Recent progress in consolidated bioprocessing. Curr Opin Biotechnol. 2012;23:396–405.
Lynd LR, van Zyl WH, McBride JE, Laser M. Consolidated bioprocessing of cellulosic biomass: an update. Curr Opin Biotechnol. 2005;16:577–83.
Durre P. Biobutanol: an attractive biofuel. Biotechnol J. 2007;2:1525–34.
Tracy BP. Improving butanol fermentation to enter the advanced biofuel market. MBio. 2012;3. pii e00518-12. doi:10.1128/mBio.00518-12.
Durre P. Fermentative butanol production—bulk chemical and biofuel. Incred Anaerob Physiol Genom Fuels. 2008;1125:353–62.
Durre P. Fermentative production of butanol—the academic perspective. Curr Opin Biotechnol. 2011;22:331–6.
Papoutsakis ET. Engineering solventogenic clostridia. Curr Opin Biotechnol. 2008;19:420–9.
Lutke-Eversloh T, Bahl H. Metabolic engineering of Clostridium acetobutylicum: recent advances to improve butanol production. Curr Opin Biotechnol. 2011;22:634–47.
Atsumi S, Cann AF, Connor MR, Shen CR, Smith KM, Brynildsen MP, Chou KJ, Hanai T, Liao JC. Metabolic engineering of Escherichia coli for 1-butanol production. Metab Eng. 2008;10:305–11.
Jang YS, Lee J, Malaviya A, Seung do Y, Cho JH, Lee SY. Butanol production from renewable biomass: rediscovery of metabolic pathways and metabolic engineering. Biotechnol J. 2012;7:186–98.
Lan EI, Liao JC. Microbial synthesis of n-butanol, isobutanol, and other higher alcohols from diverse resources. Bioresour Technol. 2013;135:339–49.
Higashide W, Li YC, Yang YF, Liao JC. Metabolic engineering of Clostridium cellulolyticum for production of isobutanol from cellulose. Appl Environ Microbiol. 2011;77:2727–33.
Griffiths MM, Bernofsky C. Purification and properties of reduced diphosphopyridine nucleotide kinase from yeast mitochondria. J Biol Chem. 1972;247:1473–8.
Xue C, Zhao XQ, Liu CG, Chen LJ, Bai FW. Prospective and development of butanol as an advanced biofuel. Biotechnol Adv. 2013;31:1575–84.
Wiesenborn DP, Rudolph FB, Papoutsakis ET. Thiolase from Clostridium acetobutylicum ATCC 824 and its role in the synthesis of acids and solvents. Appl Environ Microbiol. 1988;54:2717–22.
Duncombe GR, Frerman FE. Molecular and catalytic properties of the acetoacetyl-coenzyme A thiolase of Escherichia coli. Arch Biochem Biophys. 1976;176:159–70.
MacLean B, Tomazela DM, Shulman N, Chambers M, Finney GL, Frewen B, Kern R, Tabb DL, Liebler DC, MacCoss MJ. Skyline: an open source document editor for creating and analyzing targeted proteomics experiments. Bioinformatics. 2010;26:966–8.
Petitdemange E, Caillet F, Giallo J, Gaudin C. Clostridium-cellulolyticum sp-nov, a cellulolytic, mesophilic species from decayed grass. Int J Syst Bacteriol. 1984;34:155–9.
Tracy BP, Jones SW, Fast AG, Indurthi DC, Papoutsakis ET. Clostridia: the importance of their exceptional substrate and metabolite diversity for biofuel and biorefinery applications. Curr Opin Biotechnol. 2012;23:364–81.
Deana A, Belasco JG. Lost in translation: the influence of ribosomes on bacterial mRNA decay. Genes Dev. 2005;19:2526–33.
Pfleger BF, Pitera DJ, Smolke CD, Keasling JD. Combinatorial engineering of intergenic regions in operons tunes expression of multiple genes. Nat Biotechnol. 2006;24:1027–32.
de Smit MH, van Duin J. Control of translation by mRNA secondary structure in Escherichia coli. A quantitative analysis of literature data. J Mol Biol. 1994;244:144–50.
Smolke CD, Keasling JD. Effect of gene location, mRNA secondary structures, and RNase sites on expression of two genes in an engineered operon. Biotechnol Bioeng. 2002;80:762–76.
Bokinsky G, Peralta-Yahya PP, George A, Holmes BM, Steen EJ, Dietrich J, Lee TS, Tullman-Ercek D, Voigt CA, Simmons BA, Keasling JD. Synthesis of three advanced biofuels from ionic liquid-pretreated switchgrass using engineered Escherichia coli. Proc Natl Acad Sci USA. 2011;108:19949–54.
Nielsen DR, Leonard E, Yoon SH, Tseng HC, Yuan C, Prather KL. Engineering alternative butanol production platforms in heterologous bacteria. Metab Eng. 2009;11:262–73.
Berezina OV, Zakharova NV, Brandt A, Yarotsky SV, Schwarz WH, Zverlov VV. Reconstructing the clostridial n-butanol metabolic pathway in Lactobacillus brevis. Appl Microbiol Biotechnol. 2010;87:635–46.
Kopke M, Held C, Hujer S, Liesegang H, Wiezer A, Wollherr A, Ehrenreich A, Liebl W, Gottschalk G, Durre P. Clostridium ljungdahlii represents a microbial production platform based on syngas. Proc Natl Acad Sci USA. 2010;107:13087–92.
Lan EI, Ro SY, Liao JC. Oxygen-tolerant coenzyme A-acylating aldehyde dehydrogenase facilitates efficient photosynthetic n-butanol biosynthesis in cyanobacteria. Energy Environ Sci. 2013;6:2672–81.
Petitdemange H, Cherrier C, Raval R, Gay R. Regulation of the NADH and NADPH-ferredoxin oxidoreductases in clostridia of the butyric group. Biochim Biophys Acta. 1976;421:334–7.
Nagarajan H, Sahin M, Nogales J, Latif H, Lovley DR, Ebrahim A, Zengler K. Characterizing acetogenic metabolism using a genome-scale metabolic reconstruction of Clostridium ljungdahlii. Microb Cell Fact. 2013;12:118.
Shen CR, Lan EI, Dekishima Y, Baez A, Cho KM, Liao JC. Driving forces enable high-titer anaerobic 1-butanol synthesis in Escherichia coli. Appl Environ Microbiol. 2011;77:2905–15.
Shen CR, Liao JC. Metabolic engineering of Escherichia coli for 1-butanol and 1-propanol production via the keto-acid pathways. Metab Eng. 2008;10:312–20.
Yu M, Zhang Y, Tang IC, Yang ST. Metabolic engineering of Clostridium tyrobutyricum for n-butanol production. Metab Eng. 2011;13:373–82.
Li Y, Tschaplinski TJ, Engle NL, Hamilton CY, Rodriguez M Jr, Liao JC, Schadt CW, Guss AM, Yang Y, Graham DE. Combined inactivation of the Clostridium cellulolyticum lactate and malate dehydrogenase genes substantially increases ethanol yield from cellulose and switchgrass fermentations. Biotechnol Biofuels. 2012;5:2.
Coleman D, Gathergood N. Biodegradation studies of ionic liquids. Chem Soc Rev. 2010;39:600–37.
Ranke J, Molter K, Stock F, Bottin-Weber U, Poczobutt J, Hoffmann J, Ondruschka B, Filser J, Jastorff B. Biological effects of imidazolium ionic liquids with varying chain lengths in acute Vibrio fischeri and WST-1 cell viability assays. Ecotoxicol Environ Saf. 2004;58:396–404.
Pienkos PT, Zhang M. Role of pretreatment and conditioning processes on toxicity of lignocellulosic biomass hydrolysates. Cellulose. 2009;16:743–62.
Nakayama S, Kiyoshi K, Kadokura T, Nakazato A. Butanol production from crystalline cellulose by cocultured Clostridium thermocellum and Clostridium saccharoperbutylacetonicum N1-4. Appl Environ Microbiol. 2011;77:6470–5.
Li MZ, Elledge SJ. Harnessing homologous recombination in vitro to generate recombinant DNA via SLIC. Nat Methods. 2007;4:251–6.
Jennert KCB, Tardif C, Young DI, Young M. Gene transfer to Clostridium cellulolyticum ATCC 35319. Microbiology UK. 2000;146:3071–80.
Stergachis AB, MacLean B, Lee K, Stamatoyannopoulos JA, MacCoss MJ. Rapid empirical discovery of optimal peptides for targeted proteomics. Nat Methods. 2011;8:1041–3.
Armando JW, Boghigian BA, Pfeifer BA. LC-MS/MS quantification of short-chain acyl-CoA’s in Escherichia coli demonstrates versatile propionyl-CoA synthetase substrate specificity. Lett Appl Microbiol. 2012;54:140–8.
Zha W, Rubin-Pitel SB, Shao Z, Zhao H. Improving cellular malonyl-CoA level in Escherichia coli via metabolic engineering. Metab Eng. 2009;11:192–8.
SMG and SJ designed the experiments. SMG, AL and AHWJ performed the cloning work. SMG and AHWJ performed the transformation and cultivation of Clostridium cellulolyticum, as well as the chemical analysis (GC-Analysis) of the fermentation broth. BE performed the targeted proteomics and metabolite analysis. SMG and SJ wrote the manuscript. SJ conceived the project. All authors read and approved the final manuscript.
Funding for the research was provided by the BMBF through the BioEnergie 2021 program. We thank Bernhard Guentner for help in cloning the pM9 plasmid and Simone Jansen for technical assistance.
The authors declare that they have no competing interests.