Production of high concentrated cellulosic ethanol by acetone/water oxidized pretreated beech wood
© The Author(s) 2017
Received: 6 December 2016
Accepted: 17 February 2017
Published: 28 February 2017
Lignocellulosic biomass is an abundant and inexpensive resource for biofuel production. Alongside its biotechnological conversion, pretreatment is essential to enable efficient enzymatic hydrolysis by making cellulose susceptible to cellulases. Wet oxidation of biomass, such as acetone/water oxidation, that employs hot acetone, water, and oxygen, has been found to be an attractive pretreatment method for removing lignin while producing less degradation products. The remaining enriched cellulose fraction has the potential to be utilized under high gravity enzymatic saccharification and fermentation processes for the cost-competing production of bioethanol.
Beech wood residual biomass was pretreated following an acetone/water oxidation process aiming at the production of high concentration of cellulosic ethanol. The effect of pressure, reaction time, temperature, and acetone-to-water ratio on the final composition of the pretreated samples was studied for the efficient utilization of the lignocellulosic feedstock. The optimal conditions were acetone/water ratio 1:1, 40 atm initial pressure of 40 vol% O2 gas, and 64 atm at reaction temperature of 175 °C for 2 h incubation. The pretreated beech wood underwent an optimization step studying the effect of enzyme loading and solids content on the enzymatic liquefaction/saccharification prior to fermentation. In a custom designed free-fall mixer at 50 °C for either 6 or 12 h of prehydrolysis using an enzyme loading of 9 mg/g dry matter at 20 wt% initial solids content, high ethanol concentration of 75.9 g/L was obtained.
The optimization of the pretreatment process allowed the efficient utilization of beech wood residual biomass for the production of high concentrations of cellulosic ethanol, while obtaining lignin that can be upgraded towards high-added-value chemicals. The threshold of 4 wt% ethanol concentration that is required for the sustainable bioethanol production was surpassed almost twofold, underpinning the efficient conversion of biomass to ethanol and bio-based chemicals on behalf of the biorefinery concept.
KeywordsBeech wood Wet oxidation Ethanol fermentation Enzymatic liquefaction High gravity
Lignocellulosic biomass feedstocks have garnered a lot of interest, as they constitute a profuse resource for production of biofuels and other high-added-value bio-based materials. Biofuel production from lignocellulosic biomass, such as agricultural or forestry residues, via enzymatic pathways mainly comprises pretreatment, enzymatic saccharification, and fermentation. Pretreatment stands to be the first step to overcome the complexity and recalcitrance of lignocellulosic biomass, rendering cellulose vulnerable to enzymatic hydrolysis .
The pretreatment of lignocellulosic biomass is also the costliest part of the process for the production of biofuels. Lignin surrounds cellulose and hemicellulose, essentially making biomass highly recalcitrant to pathogens, microorganisms, and enzymes . One of the pretreatments that have been investigated in the past is the hot compressed water (HCW) treatment also known as hydrothermal treatment, thermohydrolysis, and autohydrolysis. The main aim is to hydrolyze and remove hemicellulose, so as to enhance the fermentability of the biomass and efficiency of the enzymatic processes. Zhu et al. reported that the hemicellulose hydrolysis resulted in pore size and substrate-specific surface increase, thus facilitating the access of cellulase on the cellulose structure . It has also been shown that removing the acetyl groups found on hemicellulose chains can enhance the enzymatic hydrolysis yields of the substrate . However, during hydrolysis of hemicellulose into monosaccharides, there is the simultaneous cleavage of beta-O-4 linkages and b-ethers bonds of lignin and lignin-hemicellulose bonds resulting in the release of phenolic compounds and lignin oligomers that are inhibitors for the downstream enzymatic processes [5, 6]. Therefore, removing them along with the lignin that enhances the recalcitrance of biomass towards enzymes can greatly benefit the fermentation of the resulting substrates.
Among the pretreatment methods that have attracted interest lately are the organosolv processes, which employ organic solvents for removal of the lignin fraction. A wide variety of processes, solvents, and parameters have been investigated ranging from the standard Milox process to combining chemical and physicomechanical pretreatment methods [7, 8]. The Milox process involves delignifying the biomass by treating it with formic and/or acetic acid coupled with hydrogen peroxide so as to produce highly oxidative peroxy acids that cleave the lignin bonds and depolymerize it. The main advantages of these methods are that the solvents and materials can be recovered and reused, and degradation of the dissolved fractions is minimized allowing for their use for production of high-added-value chemicals, such as phenols and hydroxymethylfurfural. In addition, the produced pulps are more easily fermented reducing the overall biofuel production process cost.
Wet oxidation of biomass employing hot water, alkali, and oxygen has also been found to be an interesting pretreatment method. Compared to steam explosion, it has been found to produce much less degradation products, such as 2-furfural and 5-hydroxy methyl-2-furfural compounds, that are well-known inhibitors of microbial growth [9, 10]. As a further development, lately a new process of acetone/water oxidation (AWO) has been developed. In this process, an acetone/water mixture is used instead of water, without alkali use. Very few papers report the effect of this treatment on biomass, but it appears to combine the advantages of wet oxidation such as low temperature and low yield of degradation products in one stage process while achieving much higher delignification of the biomass. Gong et al. reported that the AWO proved to be the most selective in delignifying both sugar maple and hot water extracted sugar maple . The same group successfully delignified Paulownia spp. wood with the same method, achieving degrees of delignification (DD) up to 93.6% in a single-stage AWO. They also found that the lignin produced was of high quality, containing no sulfur or inorganic compounds typically found in Kraft produced lignin. Jafari et al. used a mixture of 50 vol% acetone–water solution containing 0.1 wt% of H2SO4 rather than O2, and the yield of enzymatic hydrolysis was improved to 94.2% . The use of acetone and water, two easily separable and recyclable solvents, allows for the development of a low energy intensive, low-cost, green process. Furthermore, to reduce energy demands, such as the distillation energy cost, a fermentation broth exhibiting high ethanol concentration is considered to be a prerequisite and the utilization of high-solids loading of pretreated biomass in the process seems to be the key .
High gravity (HG) saccharification and fermentation stand to be a challenging but yet crucial strategy for a cost-competing bioethanol production process. An economically feasible lignocellulosic biomass to bioethanol process is reported to require, among others, a concentration of at least 4 wt% ethanol [13, 14]. However, operating under high initial dry matter (DM) faces many challenges, mainly, due to mass transfer limitations and enzyme inhibition. The conventional stirring techniques result in inadequate mixing, preventing lignocellulolytic enzymes from interacting efficiently with the substrate, while increased end-product inhibition by sugars released during enzymatic hydrolysis leads to low saccharification yields . Alternative mixing systems, such as free-fall mixing, in combination with simultaneous saccharification and fermentation (SSF) have been proved to alleviate the issues related to HG conditions in several cases [16–19].
In the present investigation, the acetone/water oxidized pretreatment of beechwood has been employed for the efficient production of cellulosic ethanol. The pretreatment conditions were optimized by studying the effect of pressure, reaction time, temperature, and acetone-to-water ratio on the final composition of the pretreated samples, as well as in their potential for the enzymatic release of fermentable sugars. The optimized pretreatment conditions were applied for the utilization of beech wood towards the enzymatic liquefaction and saccharification at high initial solids content (20 wt%).
Results and discussion
Effect of different AWO conditions on the final composition of the pretreated samples
Biomass pretreatment with acetone/water mixtures
Αcetone/water oxidation experimental conditions
Acetone/water (wt/wt) ratio
Partial O2 pressure at reaction T (atm)
Reaction T (°C)
Reaction time (h)a
Pressure at 20 °C (atm)
Pressure at reaction T (atm)
Pulp composition and total solids, lignin, hemicellulose, and cellulose recoveries after AWO
Constituents in pulp (wt%)
Constituents recovery in solid pulp (wt%)
0, 0, 175, 2, 20
0, 8, 175, 2, 19
1:0, 0, 175, 2, 22
1:0, 4, 175, 2, 22
1:0, 9, 175, 2, 22
1:1, 0, 175, 2, 27
1:1, 10, 175, 2, 25
3:1, 10, 175, 2, 25
3:1, 23, 175, 2, 58
1:1, 25, 175, 2, 64
1:3, 25, 175, 2, 64
3:1, 29, 200, 1, 74
3:1, 31, 200, 0.5, 78
3:1, 55, 225, 0.5, 139
1:1, 10, 175, 2, 24
3:1, 10, 175, 2, 25
Finally, for runs 3–5, the biomass was treated with 100% acetone employing N2, 20 vol% O2 and 40 vol% O2 (partial O2 pressures are shown in Table 2). Apart from a slight reduction in the lignin content, there was no significant change in the biomass content. The lack of water and the hydrolysis effect that it induces was apparent. It is, therefore, clear that water is needed, even at a small amount to initiate the hydrolysis of hemicellulose, and the cleavage of lignin-hemicellulose linkages that can lead to pronounced removal of both lignin and hemicellulose.
Effect of O2 rich atmosphere
To test the effect of an O2 rich atmosphere, runs 6 and 7 employed a 1:1 ratio of acetone/water at 175 °C, treatment time of 2 h under an inert (run no. 6), and a 40 vol% O2 rich atmosphere (run no. 7). Using a mixture of acetone/water rather than the pure solvents had a significant effect, which can be clearly seen by the analysis of the pretreated biomasses (Table 2). In both cases, a synergistic effect was observed, since lignin and hemicellulose contents decreased with a consequent increase in cellulose in the resulting pulp. On one hand, the water was responsible for hydrolyzing hemicellulose, possibly disrupting its linkages with lignin achieving its partial depolymerization . This allowed the acetone to solubilize the released partly depolymerized lignin, removing it from the solid biomass that, in turn, facilitated the further disruption of lignin-hemicellulose bonds. In the case of run no. 7 where the O2 partial pressure was higher, a further decrease in the lignin content was noted.
Lignin is a complex three-dimensional polymer with phenolic derivatives building units such as p-coumaryl, coniferyl, and sinapyl alcohol linked to each other by different carbon–carbon and ether linkages . These have been found to be very reactive under wet oxidation conditions, making lignin a reactive molecule . Ether linkages are broken more easily under oxidative conditions, depolymerizing lignin to lower molecular weight (MW) oligomers that may be dissolved much easier by solvents like acetone. Changing the acetone/water ratio to 3:1 (run no. 8) had similar effects. Again, both lignin and hemicellulose decreased; however, the lower water concentration resulted in decreased hydrolysis of hemicellulose that, in turn, affected lignin solubilization. It should be mentioned that O2 partial pressure was much lower (40 vol%,) under low final pressure of around 20 atm; therefore, the oxidation conditions were not very severe. Typically, 100% O2 gas is used to enhance delignification and maintain a low overall pressure, similar to acetone/water oxidation for the delignification of Paulownia spp. . To enhance the oxidative effect of O2 atmosphere, it was decided to raise the pressure at the reaction temperature at 58 atm, which corresponded to around 24 atm of O2 (40 vol% O2) partial pressure. Using a mixture of N2/O2 rather than pure O2 has the added benefit of employing a lower cost gas but may result in a need for increased pressure. In future work, a techno-economic analysis will reveal the best case scenario, still it is very promising that delignification is so effective even with a N2/O2 mixture.
Effect of acetone on water ratio
In addition to the above, the effect of acetone-to-water ratio on hemicellulose hydrolysis and removal of lignin was investigated (runs 9–11). The pressure under the reaction conditions increased to 58–64 atm (corresponding O2 partial pressure was 23–25 atm) to enhance the oxidative effect as explained above. Run no. 10, which employed the 1:1 acetone/water ratio, had a significant decrease in both lignin and hemicellulose with 2.2 and 10.8 wt%, respectively, in the resulting pulp. This corresponded to more than 90% of lignin removal. The resulting pulp had a cellulose content of 85.9 wt%, making it a very good feedstock for downstream enzymatic processes. Compared to run no. 7 where the low pressure of ~25 atm was used, the difference in the delignification efficiency was significant and is attributed to the increased partial pressure of the O2 that enhanced the depolymerization of lignin. This is in accordance to what has been reported in literature for wet oxidation process, where pure water is used as solvent. Martín and Thomsen  treated sugarcane, rice, cassava, and peanuts residues and concluded that an increase in O2 pressure resulted in higher delignification. Arvaniti et al. pretreated rape straw by wet oxidation and also found that increasing the O2 pressure removed more lignin overall from the solid pulp and also had a positive effect in the downstream enzymatic process .
Effect of temperature and pretreatment time
To investigate the effect of temperature, runs 12, 13, and 14 investigated higher temperatures of 200 and 225 °C. The ratio of acetone/water was 3:1 for all runs. Due to the increase in temperature and consequently in pressure (Table 1), the reaction time decreased to 1 and 0.5 h asserting that cellulose would not be degraded. The pulp resulting from run no. 12 at 200 °C and 1 h reaction time had a lower hemicellulose content compared to run no. 9 at 175 °C and 2 h. Hence, the hemicellulose was more efficiently hydrolyzed. Still, the lignin content increased significantly from 4.7 wt% for run no. 9–11.1 wt% for run no. 12. Decreasing the reaction time to 0.5 h, the hemicellulose content increased as expected, since less time was given for the system to hydrolyze it. However, the lignin content decreased, indicating a shift in the delignification mechanism. Hayn et al. and Saddler et al. have found that treating biomass with wet oxidation at 200 °C or more resulted in the decrease of the enzymatic hydrolysis of the resulting pulp. This was attributed to a partial melting of the lignin and coating of the cellulose [27, 28]. The reduced time in run no. 13 resulted in better DD, possibly because the lignin was not allowed to repolymerise on the pulp. Finally, run no. 14 employed the short reaction time of 0.5 h at 225 °C. The DD was not altered significantly; however, the elevated temperature resulted in a decrease in the hemicellulose and hence an overall increase in the cellulose content of the pulp.
In an effort to maximize the DD while maintaining a high cellulose recovery in the produced pulp, a two-stage pretreatment was also tested. Essentially, the biomass was first hydrolyzed to achieve hemicellulose hydrolysis under the conditions of run no. 1. This substrate was then treated at two different AWO conditions corresponding to runs 7 and 8 (Table 1). The combination of the aforementioned conditions resulted in runs 15 and 16. The pulps produced had low hemicellulose content, while lignin was 9 and 14 wt%, respectively. Runs 7 and 8 did not remove lignin and hemicellulose efficiently, mainly due to the low O2 partial pressure used. In the case of the two-stage process, the removal of both lignin and hemicellulose improved significantly. Cellulose recovery is deemed to be satisfactory for a two-stage process at 80 wt% on initially available cellulose. Still, comparing the two-stage process runs, the single-stage pretreatment can remove both lignin and hemicellulose more efficiently, while maintaining high cellulose recovery (run no. 10, 91.6 wt%) under optimal conditions. Gong et al. found that hot water extraction (HWE) carried out prior to AWO treatment was very favorable for Paulownia tomentosa and Paulownia elongata biomass, which is in accordance with our results with respect to DD and hemicellulose removal . Gong et al. attributed this beneficial effect to changes in the physicochemical structure of wood, such as increase in porosity, lower MW of residual lignin, and a weaker association between lignin and carbohydrates in the extracted wood. On the other hand, it has been reported that increasing the pretreatment severity of HWE may lead to lignin reacting with other degradation products [29, 30]. In addition, Ko et al. found that by increasing the pretreatment time of HWE, the acid insoluble lignin (AIL)/acid soluble lignin (ASL) ratio increased indicating changes in the lignin’s chemical structure . The main drawback in the case of the two-stage pretreatment is a decrease in the cellulose recovery.
Pulp and lignin quality
Apart from cellulose, hemicellulose, and lignin contents measured in the resulting pulps, the crystallinity index (CI) of select pulps was also measured. Specifically, pulps received from runs nos. 9, 10, and 11, were found to have CIs of 74.2, 78.7, and 74.7, respectively. Obviously, the high cellulose content found in all pulps resulted in a very crystalline material. The pulp from run no. 10, which had the highest cellulose content of 85.9 wt%, which also had the highest CI. The pulp resulting from run no. 11, which also had a high cellulose content of 84.1 wt%, had similar CI with the pulp resulting from run no. 9, which had cellulose content of 75.2 wt%. This was attributed to the higher lignin content of pulp no. 11 that is amorphous.
In addition, lignin was recovered from the acetone/water solvent mixture of several different runs. This was done via vacuum distillation. By evaporating and removing acetone, the dissolved lignin precipitated within the water. It was then filtered, washed with distilled water, and air dried for 24 h at 80 °C.
NREL analysis on acetone/water oxidation recovered lignins of beechwood
Treatment with the Milox process resulted in significant degrading of the recovered lignin, indicated by the lack of peaks at characteristic wavelengths below 1500/cm corresponding to guaiacyl, syringyl, and some methyl- and methylene-side chains typically found at 1385, 1420, and 1463/cm. In contrast, the AWO gave a lignin that appeared to be much less degraded. This is in accordance with the work of Gong et al.  in which they analyzed the recovered AWO lignin with 2D HSQC NMR and concluded that the AWO lignin was a high purity and quality lignin. Future work should focus on fully characterizing the AWO lignin, since it can be easily separated from the solvent mixture and could potentially be upgraded towards added-value chemicals as part of a holistic biorefinery approach.
Enzymatic hydrolysis and fermentation of AWOBW
Lignin removal is considered to be crucial for enhancing ethanol concentrations, not only by providing a material with high glucan content but also by rendering it more vulnerable to cellulolytic enzymes. In addition, non-productive binding of cellulase and β-glucosidase to lignin could be evaded at a great extent. Cellulolytic enzymes adsorption onto lignin is reported to have a significant effect on the enzymatic hydrolysis of lignocellulosic biomass resulting in reduced efficiency [33–36].
It was decided to test the suitability of different acetone/water oxidized biomasses for enzymatic hydrolysis and SSF. Overall, six different substrates were chosen, corresponding to runs 8, 9, 10, 11, 12, and 13. These substrates were produced over a different range of pressure, acetone/water ratio, temperature, and reaction time, and were found to have a range of cellulose, hemicellulose, and lignin contents. Studying them in comparison to the untreated material in downstream enzymatic processes will allow the evaluation of the pretreatment process from the total reducing sugars (TRS), glucose and ethanol production point of view.
Effect of enzyme loading on the saccharification of AWOBW
Enzyme cost contribution in bioethanol production is not negligible; thus, changes should be primarily focused in decreasing enzyme loading at the process . Therefore, enzyme loading effect investigation is crucial to achieve high saccharification yields without using an excess of enzyme dosage. To examine the effect of enzyme loading on glucose release (g/L), enzyme loads from 6 to 12 mg/g DM were used to hydrolyze AWOBW at 13 wt% solids content.
A decrease in glucose concentration of 4, 9, and 6% was noted for runs 9, 10, and 11, respectively, at 9 mg/g DM enzyme loading comparing to that of 12 mg/g DM. The use of 6 mg/g DM of enzyme loading led to a further decrease in glucose release of 27 (run 9), 21 (run 10), and 13% (run 11). Therefore, the glucose concentration difference was much lower between enzyme loadings of 9 and 12 mg/g DM than that between 6 and 9 mg/g DM. Hence, even though the enzyme loading of 12 mg/g DM resulted in the highest glucose releases after 48 h (86.5, 93.1, and 64.6 g/L from runs 9, 10, and 11, respectively) and cellulose conversions (69.0, 65.1, and 46.1%), the enzyme loading of 9 mg/g DM was selected for the experiments of enzymatic saccharification and SSF of AWOBW samples.
Comparing the release of glucose after 48 h between runs 9, 10, and 11, regardless of the enzyme loading, it is noted that run 11 had the lowest, while run 10 presented the highest glucose release in all cases. The AWOBW pulp used in run 11 had the same cellulose content as run 10, about half the content in hemicellulose and almost five times higher lignin content (Table 2). It would seem, therefore, that the critical factor in glucose release is the lignin content rather than the hemicellulose content. This is also confirmed by the release of glucose in the case of run 9, which actually has a lower cellulose content, a higher hemicellulose content but also about three times less lignin content compared to run 11. Therefore, to achieve high glucose release and cellulose conversion, the lignin content should be minimized.
Evaluation of AWOBW for the production of bioethanol
Screening of AWOBW samples, corresponding to runs 8–13, with maximum ethanol concentration (g/L) as a response, was conducted to determine the AWO conditions that lead to the highest ethanol concentration in the fermentation broth. The screening experiments were carried out on small scale in 100-mL Erlenmeyer flasks at selected enzyme loading (9-mg/g DM) employing SSF process with a 12-h prehydrolysis step at 14.5 wt% solids content.
Effect of solids content on cellulose conversion
Fermentation of liquefacted AWOBW at high-solids content
Moreover, the decrease in slurry’s viscosity, consisting of 20 wt% AWOBW, during the liquefaction/saccharification step was measured using an oscillatory viscometric technique with a parallel roughened plate system. The initial apparent viscosity was found to be 1.4 kPa s and rapidly decreased to 0.2 kPa s after 2 h of enzymatic hydrolysis remaining fairly stable until the end of the liquefaction/saccharification step. The decrease of 86.4% in viscosity in only 2 h shows the potential of AWOBW to be used effectively in high gravity processes.
The addition of extra enzyme loading (4.5 and 9 mg/g DM) prior to the SSF process was also investigated, aiming at the increase in ethanol production yield. Maximum ethanol concentration was found to be 66.7 ± 0.5 g/L after 120 h of SSF in the case of adding enzyme load of 4.5 mg/g DM for the 6-h liquefacted AWOBW, exhibiting a difference of 28.4 g/L of ethanol comparing to the 12-h liquefacted AWOBW (Fig. 7b). The addition of extra 9 mg/g DM of enzyme load resulted in a decrease in ethanol production with a final concentration of 60.3 ± 4.5 g/L in the case of the 6-h liquefacted AWOBW. When it comes to the 12-h liquefacted AWOBW, a difference of 24.4 g/L in final ethanol concentration was noted (Fig. 7c). These results indicated that enzyme addition probably led to an increase in glucose levels beyond a threshold where yeast cells exhibited low viability. Besides that, high enzyme loadings accumulated by adding extra enzyme prior to the SSF process could negatively affect cell viability due to additives that are present in commercial lignocellulolytic mixtures, such as sorbitol or glycerol . These results are also in agreement with similar findings by Zhao et al. where an increase in cellulase loading from 10 to 20 FPU/g solid led to lower ethanol production rates for both batch and fed-batch SSF processes .
Comparison of bioethanol production from various kinds of lignocellulosic biomass at high-solids content
Solids content (wt%)
Enzyme loading (FPU/g DM)
Ethanol concentration (g/L)
Ethanol productivity (g/L·h)
Ethanol yieldf (%)
Dilute acid hydrolysis-alkaline extraction
Acetic acid-catalysed hydrothermal
Empty palm fruit bunch
Dilute acid-dilute alkali
Sweet sorghum bagasse
It is worth mentioning that several of the studies that are presented in Table 4 include media sterilization and/or nutrient addition, which boosts final ethanol concentrations, but on the other hand contributes to a final process cost increase. Furthermore, to enhance ethanol production, the use of enzymes such as laccases has been reported. Alvira et al. produced 58.6 g/L ethanol from steam exploded wheat straw at 25 wt% solids content when prehydrolysis step supplemented with laccase, which led to a significant final ethanol concentration increase .
In the present work, the potential of a woody biomass, specifically beechwood, for the production of cellulosic ethanol was investigated, through the optimization of the acetone/water oxidized pretreatment and SSF process. The optimal pretreatment conditions were acetone/water ratio 1:1, 40 atm initial pressure of 40 vol% O2 gas (20 °C) and 64 atm at reaction temperature of 175 °C for 2 h incubation. These pretreatment conditions allowed the isolation of lignin, which was found to be intact and could, therefore, potentially lead to high-added-value products, such as phenols and aromatics in a holistic biorefinery approach. The subsequent liquefaction and saccharification process of the pretreated BW feedstock at high-solids content allowed the production of high ethanol concentration (75.9 ± 2.0 g/L). To the authors’ knowledge, the obtained ethanol concentration is the highest reported in literature utilizing BW residual biomass, underpinning the potential of the pretreatment and fermentation process followed for the efficient conversion of biomass to ethanol and bio-based chemicals.
Lignocellulosic biomass used as a feedstock in the experiments of the current study was a commercially available beech wood (BW) with particle size 150–500 μm (Lignocel® HBS 150-500) and was handled, as described by Kalogiannis et al. .
Strains and enzymes
Saccharomyces cerevisiae strain Ethanol Red®, developed for the industrial ethanol industry by Fermentis (Marcq-en-Barœl, France) exhibiting high ethanol tolerance and cell viability during HG fermentation, was employed in SSF experiments. Commercial enzyme solution Cellic® CTec2 was obtained from Novozymes A/S (Bagsværd, Denmark) and used for the liquefaction and saccharification of acetone/water oxidation pretreated beech wood (AWOBW). Filter paper activity was determined according to Ghose  and found to be 84 FPU/mL. Protein content was measured using the Bradford assay  and was 90 mg/mL. All other chemicals and reagents were of analytical grade.
Acetone/water oxidation pretreatment
AWO of biomass was carried out in a Hastelloy C-276 Parr autoclave with a volume of 975 mL. 50 g of solid feedstock were fed into the reactor and 500 g of an acetone/distilled water mixture were then poured at a ratio of liquid to solid 10:1. The reactor was tightly sealed and pressurized up to 40 atm with a N2/O2 mixture. A Parr Model 4848 reactor controller was used to control the temperature inside the reactor. Uniform heating and temperature was ensured by mixing of the suspension with a propeller type agitator rotating at 150 rpm. The temperature was set at 175 °C for a reaction time of 2 h in all cases. Reaching the desired temperature took typically 15 min; this was defined as time zero. After the prescribed reaction time, the cool down time was minimized to around 15 min by cooling the reactor with air externally and internally with water that was circulated through a cooling coil. The solid residue was filtered from the liquid phase, washed with 250 g of acetone, and dried overnight in an oven at 80 °C. A round of wash with distilled water and dry overnight was followed.
Among the parameters studied were the pressure, reaction time, temperature, and acetone-to-water ratio. Specifically, two different pressures were employed. The autoclave was pressurized at low pressure (LP) of 8.5 atm and at high pressure (HP) of 40 atm at 20 °C. Final pressure depended on the reaction temperature. The temperatures studied were 175, 200, and 225 °C for reaction times of 2, 1, and 0.5 h, respectively. In addition, the biomass was treated hydrothermally with 100% water and with 100% acetone under either an inert atmosphere (N2) or pressurized with 40 vol% O2. The acetone-to-water ratio was also investigated. Apart from the runs that employed 100% water or acetone the 3:1, 1:1, and 1:3 acetone:water ratios were tested as well. All experimental conditions are presented in Table 1. All runs were repeated twice and the mean values are reported. The resulting pulps were dried and weighed, while the original biomass and the resulting pulps were analyzed by the NREL method to determine (see “Analytical methods” section) cellulose, hemicellulose, and lignin contents. Standard deviation for the recovered pulps was below ±1.5%. This allowed for the determination of the recoveries of each biomass constituent in the solid pulp. The delignification degree (DD) can be calculated as 100% lignin recovery (%).
TRS concentration was determined according to dinitro-3,5-salicylic acid (DNS) method  and glucose was measured according to commercial enzyme preparation of glucose oxidase/peroxidase (GOD/PAP) assay. The cellulose, hemicellulose, lignin, and ash contents of lignocellulosic biomass were determined according to the procedures provided by National Renewable Energy Laboratory (NREL; Golden, CO, USA) . Ethanol produced during the SSF was analyzed by a high-pressure liquid chromatography (HPLC) apparatus consisting of a fully integrated solvent delivery system (LC-20AD; Shimadzu, Kyoto, Japan) coupled with a refractive index detector (RID 10A; Shimadzu), an auto sampler (SIL-20A; Shimadzu), and a computer-based integration system (LCsolution Version 1.24 SP1; Shimadzu). An Aminex HPX-87H (300 × 7.8 mm, particle size 9 μm; Bio-Rad, Hercules, CA, USA) chromatography column was used. Mobile phase was 5 mM sulphuric acid in degassed HPLC grade water at a constant flow rate of 0.6 mL/min and the column temperature was maintained at 40 °C using a column heater (Merck Millipore, Darmstadt, Germany).
Fourier transform infrared spectroscopy (FTIR) analysis was employed for further characterization of the lignin samples’ structure. Details may be found elsewhere . X-ray diffraction analysis was done on a Siemens D500, copper ray with a Nickel filter (λ = 1.5406 Å, voltage 40 kV, intensity 30 mA). The angle 2θ was between 5° and 50° with a step 0.04 step time 2 s.
Enzymatic liquefaction and saccharification of AWOBW
Enzymatic saccharification of AWOBW samples was carried out in 100-mL Erlenmeyer flasks (small scale) in an orbital shaker (Zhicheng, Shanghai, China). BW loadings of 13 wt% (6–12 mg Cellic® CTec2/g DM) and 7.4–13 wt% (9 mg Cellic® CTec2/g DM) in 100-mM citrate–phosphate buffer at pH 5.0 were employed for investigating the effect of enzyme loading and solids content on cellulose conversion, respectively. Saccharification was performed for 48 h at 50 °C and 200 rpm. Microbial contaminations were prevented by the addition of 0.02% (w/v) sodium azide. Samples were taken at different time intervals and soluble sugars were determined, to estimate cellulose and total polysaccharides hydrolysis. Each experiment was carried out in duplicates. Error bars in figures represent the standard deviation between experimental measurements.
AWO pretreated samples at 14.5 wt% loading underwent a liquefaction step in 100-mL Erlenmeyer flasks in an orbital shaker at 50 °C, in 100-mM citrate–phosphate buffer pH 5.0 for 12 h using 9-mg/g DM of Cellic® CTec2. After the liquefaction step, slurry temperature was adjusted to 35 °C for the subsequent fermentation process.
Liquefaction and saccharification of AWOBW at high initial DM content of 20 wt% to achieve high sugar concentration were enabled employing a free fall mixer (large scale), consisting of two vertically placed, cylindrical liquefaction chambers of 6 cm in width and a diameter of 25 cm with the ability to rotate for proper material mixing . Rotation speed was adjusted at 7 rpm and was changing from clock to anti-clock wise every 2 min. The liquefaction chambers were maintained at 50 °C by an oil-filled heating jacket. Enzyme load was 9-mg/g DM of Cellic® CTec2 at 100-mM citrate–phosphate buffer pH 5.0. The duration of liquefaction-saccharification step was either 6 or 12 h.
The liquefaction step of AWOBW catalysed by Cellic® CTec2 was carried out in the free-fall mixing apparatus described previously. For the determination of the viscosity, aliquots of the liquefacted AWOBW were taken in different time intervals and apparent viscosities of slurries were measured with an Anton Paar Physica MCR rheometer (Anton Paar Gmbh, Styria, Austria), as described previously . Apparent viscosities during enzymatic hydrolysis were compared at shear rate of 0.03/s (ω of 60 rad/s). The parallel plates’ diameter was 25 mm and the gap between them was ≈2 mm.
Simultaneous saccharification and fermentation experiments
Fermentations of non-sterilized liquefacted AWOBW at 14.5 (small scale) and 20 wt% DM (large scale) were performed in 100-mL Erlenmeyer flasks at pH 5.0 and temperature of 35 °C in an orbital shaker (80 rpm). S. cerevisiae strain Ethanol Red®, corresponding to 15 mg/g DM, was used for the anaerobic fermentation without the addition of extra nutrients in the fermentation broth. Samples were taken at 0, 12, 24, 48, 72, 96, and 120 h and were analyzed for ethanol. The ethanol yield was calculated according to the method of Zhang and Bao  for high-solids and high ethanol concentration SSF process. Each trial was carried out in duplicates. Error bars in figures represent the standard deviation between experimental measurements.
acid insoluble lignin
acid soluble lignin
acetone/water oxidation pretreated beech wood
degrees of delignification
Fourier transform infrared spectroscopy
hot compressed water
high-pressure liquid chromatography
hot water extraction
national renewable energy laboratory
simultaneous saccharification and fermentation
total reducing sugars
ET conceived and designed the experiments; KK and AL conceived the pretreatment process; CK and AK performed the experiments; ET, CK, and KK wrote the manuscript. All authors read and approved the final manuscript.
The authors are also grateful to Novozymes A/S for providing Cellic® CTec2, and to Lesaffre for providing Ethanol Red®.
The authors declare that they have no competing interests.
Availability of data and materials
Consent for publication
All authors consented on the publication of this work.
CK and ET wish to acknowledge financial support of this research by the Greek State Scholarships Foundation (Research Projects for Excellence IKY/Siemens).
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