- Open Access
A novel solid state fermentation coupled with gas stripping enhancing the sweet sorghum stalk conversion performance for bioethanol
Biotechnology for Biofuels volume 7, Article number: 53 (2014)
Bioethanol production from biomass is becoming a hot topic internationally. Traditional static solid state fermentation (TS-SSF) for bioethanol production is similar to the traditional method of intermittent operation. The main problems of its large-scale intensive production are the low efficiency of mass and heat transfer and the high ethanol inhibition effect. In order to achieve continuous production and high conversion efficiency, gas stripping solid state fermentation (GS-SSF) for bioethanol production from sweet sorghum stalk (SSS) was systematically investigated in the present study.
TS-SSF and GS-SSF were conducted and evaluated based on different SSS particle thicknesses under identical conditions. The ethanol yield reached 22.7 g/100 g dry SSS during GS-SSF, which was obviously higher than that during TS-SSF. The optimal initial gas stripping time, gas stripping temperature, fermentation time, and particle thickness of GS-SSF were 10 h, 35°C, 28 h, and 0.15 cm, respectively, and the corresponding ethanol stripping efficiency was 77.5%. The ethanol yield apparently increased by 30% with the particle thickness decreasing from 0.4 cm to 0.05 cm during GS-SSF. Meanwhile, the ethanol yield increased by 6% to 10% during GS-SSF compared with that during TS-SSF under the same particle thickness. The results revealed that gas stripping removed the ethanol inhibition effect and improved the mass and heat transfer efficiency, and hence strongly enhanced the solid state fermentation (SSF) performance of SSS. GS-SSF also eliminated the need for separate reactors and further simplified the bioethanol production process from SSS. As a result, a continuous conversion process of SSS and online separation of bioethanol were achieved by GS-SSF.
SSF coupled with gas stripping meet the requirements of high yield and efficient industrial bioethanol production. It should be a novel bioconversion process for bioethanol production from SSS biomass.
The production of biofuels (largely bioethanol) from biomass has attracted much interest from governments around the world because of its higher octane number and higher heat of vaporization [1–4]. Agriculture straw biomass is the most abundant renewable resource on earth, and the annual yield is approximately 700 million tons in China [5, 6]. Of the many agriculture straws currently being investigated for energy and industry, sweet sorghum stalk (SSS) is considered as a cost-effective feedstock for bioethanol production due to its higher drought resistant ability, lower production costs, and higher biomass yield (20 to 30 dry tons/ha) compared with other straws [7–9]. SSS, which is a C4 plant, can efficiently convert sunlight into stored chemical energy by photosynthetic fixation of atmospheric CO2 to produce sugars . A large proportion of these sugars are stored either as soluble sugars or plant cell wall polymers, and hence SSS contains plentiful soluble carbohydrates (especially glucose, fructose, and sucrose) and insoluble carbohydrates (cellulose and hemicellulose), which can be converted into biofuels by microorganisms [8, 9]. Meanwhile, sweet sorghum juice accounts for a large part of SSS biomass, which not only contains abundant soluble sugars used directly as a substrate for bioethanol production, but also provides efficient nutrient supplementation for microbe fermentation [8, 10]. Therefore, SSS biomass should be the first competitor among the biological energy agriculture crops, and utilization of SSS for bioethanol production should be an effective way to reduce the process capital cost [11–14].
Previous literature has reported on bioethanol production using submerged fermentation (SmF) from sweet sorghum juice [15, 16]. The juicing process of sweet sorghum juice from SSS biomass makes the bioconversion process tedious, and hence increases the capital cost of bioethanol production. Meanwhile, there are many shortcomings of the SmF process for biofuel production from solid substrate biomass, including high pretreatment costs, relatively low volumetric productivity, hard separation and purification of products, and much effluent generation [17–19]. Generally speaking, solid state fermentation (SSF), which is defined as a microbial culture that develops on natural solid substrates or impregnated inert supports in or near the absence of free water, offers numerous advantages (such as lower energy requirements, producing lesser wastewater, environmentalfriendly, and so on) over SmF, particularly with the possibility of using solid agro-industrial residues for biofuel production [20–22]. However, few reports are available using SSF from SSS biomass for bioethanol production. A summary of literature reports on SSF of SSS for bioethanol production is shown in Table 1 [23–25]. The traditional SSF for bioethanol production from SSS biomass is similar to the traditional method of intermittent operation. However, it does not meet the requirements of large-scale intensive production of bioethanol from solid substrate biomass. During the traditional SSF process, the absolute ethanol content in solid substrate is much higher than that during SmF, and the ethanol inhibition effect on yeast cells becomes more significant [4, 26]. Since the thermal conductivity of solid substrates is very low and there is little free water in the reaction system, the removal of excess heat and the transfer of mass are other major problems for traditional SSF [18, 20]. Meanwhile, physicochemical characterization of the solid substrate biomass, including particle size and chemical composition, also apparently affect the SSF performance [17, 18].
The present study aims to systematically identify the effects of gas stripping on SSF performance of SSS solid substrates for bioethanol production compared with TS-SSF. The effects of gas stripping on the ethanol yield and the heat and mass transfer efficiency during SSF were analyzed. Ethanol stripping efficiency was considered as the key metric for evaluation of the ethanol online separation efficiency and GS-SSF performance. Fermentation conditions that might affect GS-SSF performance (including initial gas stripping time, gas stripping temperature, fermentation time, and particle thickness) were also investigated in the present study. Meanwhile, the relations of the ethanol content distribution between the gas phase by gas stripping and fermentation of the solid substrate residue were established in GS-SSF. To our knowledge, this is the first systematic study on gas stripping enhancing SSF performance from SSS for bioethanol production without physicochemical pretreatment.
Results and discussion
Composition analysis of sweet sorghum stalk (SSS)
The chemical composition of feedstock is crucial for the biomass conversion process, especially for SSF from solid substrates [1, 17, 18]. The chemical composition analysis of SSS is shown in Table 2 and expressed in total matter (TM) and dry matter (DM). The results showed that the moisture content of SSS, which is one of the most important parameters in SSF [17, 21], reached 76.2% based on TM. Previous studies confirmed that high moisture content resulted in the decrease of solid substrate biomass porosity, which in turn affected the gas transfer and exchange efficiency during SSF. On the other hand, low moisture content may lead to poor accessibility of nutrients, resulting in poor microbial growth and fermentation performance [17, 27]. Low substrate moisture content also resulted in secondary metabolite formation due to the difficulty of solute diffusion to the cells of microorganisms during SSF . The moisture content used in this study was maintained at 70% based on the experimental optimum of our previous studies. SSS contained plentiful soluble sugars (43.07% sucrose, 7.69% glucose, and 4.71% fructose based on DM), which were easily directly converted to ethanol by microbial fermentation. The total soluble sugars of SSS were obviously higher than that of the literature report [9, 14, 23], which may reflect a difference in SSS itself. The content of crude fiber, which mainly contains cellulose, hemicellulose, and lignin, was 36.34% (DM). Thus, the total carbohydrate content of SSS was apparently higher than that of other agricultural straws [4, 29]. Previous studies reported that the bioconversion efficiency of biomass is positively correlated with the amount of salts generated from the plant cell [30, 31]. The ash content of SSS reached 5.13% (DM) in the present study. It should provide inorganic salt for microbial growth which may improve microbial activity, and hence enhance microbial fermentation performance. Therefore, the results implied that SSS should be a suitable biomass for the bioconversion process of bioethanol production.
Determination of initial gas stripping time
In the present study, the evaluation of initial gas stripping time during GS-SSF for conversion of SSS into bioethanol was carried out in shake flasks. Soluble sugars in SSS were converted to CO2 and ethanol by Saccharomyces cerevisiae. Due to the fact that CO2 is the other product of the SSS conversion process for ethanol production, the ethanol production rate could be directly described by the CO2 weight loss rate [32, 33]. Therefore, the CO2 weight loss rate should be considered as the optimization objective of conversion biomass for bioethanol fermentation, which was also used as the indication of microbial activity and fermentation performance. Figure 1A shows that the CO2 weight loss rate obviously increased with the fermentation time from 0 h to 10 h, but then decreased with the fermentation time from 10 h to 30 h. The approximate maximum CO2 weight loss rate of 2.0 g/2 h was obtained at 10 h after inoculation during SSF, which indicated that the corresponding highest yeast activity and ethanol production rate should be obtained under this fermentation time. The results also implied that ethanol content in solid substrate should rapidly increase after 10 h of fermentation during SSF. The bioconversion process for bioethanol production from biomass is a typical end-product feedback inhibition process. In other words, high ethanol content reduces the fermentative activity of yeast, and hence reduces the ethanol yield and the conversion performance [26, 34]. Due to the high end-product content in solid substrate biomass during SSF, the ethanol feedback inhibition effect on yeast cells should become more significant. Thus, excess accumulation of ethanol in the solid substrate should not be permitted for the ethanol production process and the ethanol content must be very highly controlled. In the present study, gas stripping was used for online separation of ethanol from the fermentation of solid substrate residue and removing the ethanol inhibition effect during SSF. The initial gas stripping time during SSF should be the balance of the capital cost of the stripping operation and the ethanol yield or the ethanol stripping efficiency. According to the above analysis, the optimal initial gas stripping time was determined as 10 h after inoculation during SSF.
Optimization of ethanol fermentation time
The capital cost of biomass conversion for ethanol production is closely related to fermentation time , which should also obviously affect the gas stripping efficiency. Figure 1B and Figure 1C show the fermentation dynamics of TS-SSF and GS-SSF, respectively, for ethanol production from SSS. The results indicated that the ethanol content based on the DM of the solid substrate is a function of fermentation time. Ethanol content rapidly increased and sugar content obviously decreased with the fermentation time from 10 h to 24 h for TS-SSF and from 10 h to 28 h for GS-SSF after inoculation, respectively, but ethanol content then hardly increased for both TS-SSF and GS-SSF with the increase of fermentation time. This was due to the fact that the nutrition was affluent and easily obtained and utilized by yeast at the beginning of fermentation, while the available sugar content in the fermentation of solid substrate residue was low at the late stage of fermentation. The results showed that the fermentation time of the achievement of the highest ethanol content during TS-SSF was less than that of GS-SSF. It was also interesting to note that the sugar consumption rate and ethanol production rate were both lower for TS-SSF compared with that for GS-SSF. However, the ethanol content after 24 h of fermentation exhibited an opposite trend. From the fermentation point of view, the logical approach should be the selection of optimal fermentation time, leading to maximal ethanol yield based on economic analysis. To our knowledge, an increase of fermentation time obviously increases the capital cost of the bioethanol production process and the possibility of contaminative microbes. Meanwhile, the extension of fermentation time also increased the gas stripping operation cost during GS-SSF. High ethanol productivity and short fermentation time are needed, and it should be not a contradiction in ethanol production. The short-term fermentation may improve the ethanol yield due to the avoidance of end-product inhibition and ethanol volatilization and the reduction of contamination risk during SSF [22, 36]. It can also improve the utilization efficiency of equipment, and hence reduce the process capital cost. Thus, the optimal ethanol fermentation time was determined as 28 h during SSF of SSS in the present study.
Effect of temperature on online ethanol separation by gas stripping
Temperature is one of most important parameters for fermentation and ethanol separation by gas stripping in the biomass conversion process [34, 37]. Gas stripping experiments at different temperatures including 35, 45, 55, 65, and 75°C were performed with an initial ethanol content of 22% (w/w) in SSS solid substrate (Figure 2). The results clearly showed the importance of gas stripping temperature for ethanol distribution and ethanol stripping efficiency. With the increase of temperature, the ethanol content in solid substrate residue apparently decreased from 5.1% to 1.8%, while the ethanol content in the gas phase by gas stripping obviously increased from 16.9% to 20.1% (Figure 2A). The ethanol stripping efficiency increased by approximately 20% with temperature increasing from 35°C to 75°C, and the highest ethanol stripping efficiency (96.4%) was obtained at 75°C (Figure 2B). Increased temperature obviously improved the ethanol stripping efficiency because the partial pressure of ethanol in the gas phase and the ethanol diffusion rate in the pores of the solid substrate apparently increased. However, high ambient temperature increases the energy consumption and should reduce the energy utilization efficiency. Previous studies confirmed that the temperature of the solid substrate was also very critical during SSF, since it ultimately affected the activity of enzymes, growth of microbes, morphological characteristics of the solid substrate, formation of product, and mass and heat transfer [18, 38, 39]. The high temperature was helpful to online ethanol separation by gas striping, but it was harmful to yeast activity, especially when the temperature was more than 30°C, which was a contradiction during GS-SSF. In order to improve the ethanol stripping efficiency and strengthen the SSS conversion performance, thermal-tolerant alcohol active yeast were used for ethanol production during SSF in the present study. However, the fermentation temperature should be no more than 40°C. Therefore, considering all the above discussions, the optimum temperature for GS-SSF was determined as 35°C.
Effect of particle thickness on GS-SSF
Different SSS particles, including 2.0 cm long and 0.4 cm, 0.3 cm, 0.15 cm, 0.1 cm and 0.05 cm thickness, were used as solid substrate and evaluated for improving the conversion performance during GS-SSF. The effect of particle thickness on the ethanol distribution, ethanol stripping efficiency, and ethanol yield of GS-SSF were systematically investigated and the results are given in Figure 3. The results showed that the thickness of particles obviously affected the ethanol distribution and ethanol stripping efficiency during GS-SSF. The ethanol content in solid substrate residues increased by about 3.6 times with the decrease of particle thickness from 0.4 cm to 0.05 cm, which meant that the smallest particle thickness within the present particle thickness range retained the highest ethanol content during GS-SSF (Figure 3A). The possible reason for this result was that the porosity of SSS greatly decreased with the decrease of SSS particle thickness, which reduced the gas diffusion rate in the pores of the SSS pile. Furthermore, the smaller particle thickness formed more sealed chambers, which may prevent the overflow of ethanol from the solid substrate. The ethanol content in the gas phase by gas stripping increased by 16% with the decrease of particle thickness from 0.4 cm to 0.15 cm, but it then obviously decreased by 40% with the decrease of particle thickness from 0.15 cm to 0.05 cm. The highest ethanol content in the gas phase by gas stripping was about 17% at 0.15 cm particle thickness (Figure 3A). These results confirmed the above discussions of the ethanol content distribution in solid substrate residues at different particle thicknesses.
Among the several parameters, particle size, which is closely related with microbial growth and activity and the fermentation performance, is a critical factor in SSF [38, 40]. It was interesting to note that the ethanol yield apparently increased from 17% to 22% with particle thicknesses from 0.4 cm to 0.05 cm (Figure 3B). The maximum ethanol yield was obtained at the smallest particle thickness within the present particle thickness range. The reason for this phenomenon was that the particle size obviously affects the specific surface area of the solid substrate . The available surface area for microbes increased with the decrease of particle thickness. In other words, the smaller particle thickness would provide a larger surface area for microbial attack. Due to the fact that a sufficient surface area was available for adequate nutrient diffusion and transfer, the growth rate of S. cerevisiae increased, and hence the ethanol production efficiency was improved. However, the energy consumption of size reduction of biomass is higher for small particle thickness than that for large thickness. In addition, too small particle thickness may result in the adhesion and agglomeration of the solid substrate during SSF, which may reduce the solid substrate porosity and the gas diffusion rate and increase the accumulation of heat. The reduced mass and heat transfer efficiency led to the poor growth of microbes, and hence the low product yield [22, 40]. Therefore, it would be necessary to choose a suitable particle size for the biomass conversion process.
The ethanol stripping efficiency obviously decreased from 83.7% to 57.5% with particle thicknesses from 0.4 cm to 0.05 cm (Figure 3B). The maximum ethanol stripping efficiency (83.7%) was obtained at the largest particle thickness (0.4 cm). The possible reason for this result was that the particle thickness obviously affected the packing density of the biomass solid substrate and gas exchange efficiency during SSF [18, 41]. The packing density which determined the solid substrate porosity and the solid substrate bed thickness decreased with the increase of particle thickness. The smallest packing density and the highest porosity of the SSS solid substrate pile were obtained at 0.4 cm thickness. Within the present particle thickness range, the larger particle thickness provided limited surface for microbial attack compared with the smaller thickness, but it provided larger inter-particle space of the solid substrate pile. The larger inter-particle space was helpful for gas diffusion and exchange during gas stripping, and hence improved the ethanol stripping efficiency.
The results implied that the highest ethanol yield was obtained at the smallest particle thickness, but the highest ethanol stripping efficiency was obtained at the largest particle thickness. High ethanol yield was required for the bioconversion process from biomass, while stripping efficiency was a key standard for the downstream process of product separation due to the fact that the high stripping efficiency reduced the capital cost in the industrial process. As a result, the analysis of the ethanol yield and ethanol stripping efficiency combined with energy consumption of size reduction suggested that the 2.0 cm long and 0.15 cm particle thickness was more suitable for the SSS bioconversion process by GS-SSF.
Traditional static solid state fermentation (TS-SSF) versus gas stripping solid state fermentation (GS-SSF)
The effect of particle thickness on kinetic parameters of TS-SSF from SSS for ethanol production are shown in Figure 4A. The results showed that the TS-SSF performance was strongly influenced by fermentation time and particle thickness. The ethanol content in the solid substrate following the typical batch static fermentation pattern rapidly increased with fermentation time from 10 h to 20 h, and then the ethanol production rate slowed down for all particle thicknesses. One reason for this phenomenon was that the initial ethanol production rate was a function of the accessible surface area for microbes, while the slowdown of the ethanol production rate at the later stage of fermentation was due to the low nutrient content in the solid substrate and the difficulty of attacking the remaining nutrients. Another important reason for this result was that ethanol production from solid substrate biomass was an end-product feedback inhibition reaction. The high ethanol content in the solid substrate at the later stage of TS-SSF should result in a significant ethanol inhibition effect on yeast cells, which obviously reduced the ethanol productivity. When fermentation time varied from 10 h to 20 h, the ethanol content obviously increased with a particle thickness decrease from 0.4 cm to 0.05 cm. Furthermore, the smaller particle thickness also obtained higher ethanol content at the later stage of TS-SSF compared with the larger thickness. These trends were approximately similar to the GS-SSF process at different SSS particle thicknesses.
The ethanol yields during TS-SSF and GS-SSF at different particle thicknesses were compared in the present study (Figure 4B). The results showed that the ethanol yield was higher during GS-SSF than TS-SSF under the same particle thickness, and the corresponding ethanol yield increased by 6% to 10% for GS-SSF compared with TS-SSF. Previous studies reported that the mass and heat transfer was a major bottle neck for SSF, and especially for large-scale production [17, 18, 22]. During SSF, a large amount of heat was generated and the temperature gradient was formed in the solid substrate, which was directly related to the metabolic activities of the microorganisms. The solid substrate biomass used for SSF has low thermal conductivity, and hence the removal of heat from the inner solid substrate residue could be very slow and inefficient [17, 22]. Worse still, accumulation of heat was often fatal during the fermentation process because the increased temperature could affect the growth of microorganisms and the product formation. Meanwhile, the main mass transfer method in the solid substrate is molecular diffusion during TS-SSF, which obviously affects the nutrition transfer efficiency. To remove the accumulated heat and the temperature gradient in the solid substrate and strengthen the fermentation performance, aeration was introduced into the SSF process in previous studies [21, 42]. The application of gas stripping to separate ethanol under a certain temperature removed the heat generated by microbial metabolism through the strengthened gaseous phase during SSF, which improved the mass and heat transfer efficiency. Meanwhile, the gas stripping operation also provided agitation and loosened the solid substrate bed, which was not only helpful for the growth of microbes but also improved the mass and heat transfer efficiency through strengthening the solid phase during GS-SSF.
On the other hand, the ethanol content in SSF was much higher than that in SmF [21, 34, 35]. Thus, the ethanol inhibition effect on yeast becomes significant during SSF. Figure 4C shows that the ethanol content in the solid substrate residue during TS-SSF rapidly increased with fermentation time from 10 h to 28 h, and it then reached about 18% and kept at a high level at the later stage of fermentation. However, the ethanol content in the solid substrate was apparently less than 8% at 10 h and decreased from 8% to 5% with fermentation time from 10 h to 42 h after gas stripping during GS-SSF, which was obviously lower than that during TS-SSF. The results also indicated that the ethanol content per 2 h in the gas phase by gas stripping increased with fermentation time from 10 h to 20 h, and then decreased with the progress of fermentation during GS-SSF. The ethanol gas stripping rate was higher than 1.0% (w/w) per 2 h with the fermentation time from 10 h to 28 h. These results revealed that gas stripping significantly carried off the ethanol from fermentation of the solid substrate residue during GS-SSF, which obviously removed the ethanol inhibition effect. The metabolic activities of yeast were improved, leading to the increase of cell density. As a result, the solid substrate was fully utilized by yeast and the ethanol yield was apparently improved during GS-SSF compared with TS-SSF. Meanwhile, gas stripping may also result in an increase in ethanol productivity due to the reduced by-product formation by yeast metabolism during GS-SSF.
Although the bioconversion processes for bioethanol production from SSS were simplified compared with the traditional SmF process (Figure 5), TS-SSF was in accordance with the traditional method of intermittent operation. The products and the solid substrate residues should be transferred into another reactor and the distillation procedures should also be conducted after TS-SSF. These processes are very tedious and will definitely take a very long time, which obviously increased the product recovery costs during the bioethanol production process. Thus, the TS-SSF process does not meet the requirements of the low time utilization ratio and the high yield and efficiency of industrial production. In the present research, continuous operation for bioconversion of SSS biomass was achieved due to the coupling of the ethanol fermentation and the online ethanol separation through GS-SSF. During GS-SSF, the fermented mixtures were felled into the gas-stripping tank automatically because the fermenter and gas-stripping tank were linked vertically and sealed as a whole (Figure 6). From solid substrate preparation to ethanol separation, all operations were completed in the novel GS-SSF reactor, which avoided the influence of the external environment. The GS-SSF process eliminated the need for separate reactors and further simplified the bioconversion process. It also saved production time and labor and improved the product yield, and hence reduced the capital cost of the bioethanol production process.
Therefore, gas stripping strongly enhanced the SSF performance due to the removal of the ethanol inhibition effect, strengthening of mass and heat transfer, and simplification of the production process compared with TS-SSF. In the present study, SSF coupled with gas stripping (GS-SSF) was a novel SSS bioconversion process for bioethanol production compared with TS-SSF, especially compared with the traditional SmF process (Figure 5).
Our results showed that gas stripping obviously enhanced GS-SSF performance of SSS compared with TS-SSF. Optimal GS-SSF conditions of initial gas stripping time, gas stripping temperature, fermentation time, and particle thickness were 10 h, 35°C, 28 h, and 0.15 cm, respectively. Gas stripping apparently improved the ethanol yield because the ethanol inhibition effect was removed and the mass and heat transfer efficiency improved. Meanwhile, GS-SSF eliminated the need for separate reactors and further simplified the ethanol production process. Therefore, SSF of SSS coupled with gas stripping would be more suitable to improve fermentation ability, and hence reduce the capital cost of the bioconversion process compared with TS-SSF.
Materials and methods
The conversion process diagram and the novel GS-SSF reactor system
The conversion process diagram of a novel SSF coupled with gas stripping for bioethanol production from SSS at different particle thicknesses is given in Figure 5, compared with traditional bioethanol production by SmF.
The novel GS-SSF reactor system is illustrated in Figure 6. It mainly consists of a fermenter, a gas-stripping tank, two carbon adsorption columns, a condensator, a CO2 gas bottle, and a stepping motor.
Raw material preparation
The SSS used in the present study was harvested from the suburb of Beijing, China. For composition analysis, raw material was air-dried to the moisture content of 5% to 10%, and then milled by knife mill (MQF-420, BJZKRF, Beijing, China). The milled raw material was passed through a screen of 2 mm and stored in sealed bags at 4°C. For SSF, raw materials were first cut into 2.0 cm long pieces by knife mill, and then torn into 0.4 cm, 0.3 cm, 0.15 cm, 0.1 cm, and 0.05 cm thicknesses by tearing chopper (Y-S800, BJZKRF), respectively.
Microorganism and seed culture preparation
The S. cerevisiae used in this study was obtained from Hubei Angel Yeast Co., Ltd (Hubei, China). S. cerevisiae was pre-cultivated in YPD medium (20 g/L glucose, 10 g/L yeast extract, and 20 g/L peptone) at 30°C and 200 rpm for 15 h. The cells were then inoculated to secondary seed liquid culture medium consisting of 20 g/L glucose, 10 g/L yeast extract, and 20 g/L peptone, and were cultivated at 30°C and 200 rpm for 15 h. The initial optical density (OD) at 600 nm for secondary seed was 0.05.
Five different biomass particles were placed in 1.0 L shake flasks capped with rubber stoppers perforated with a syringe needle for gas release. Next, 0.5 g ammonium sulfate/100 g SSS (DM) and 0.5 g calcium chloride/100 g SSS (DM) were added and mixed evenly. The moisture content of SSS was adjusted to 70% by deionized water, and the initial pH was adjusted to 5.0. The mixture was then sterilized at 121°C for 15 min. After sterilization, 0.5 g yeast/100 g SSS (DM) was added into the mixture and mixed well, and the shake flask was then kept statically in the water bath at 35°C. The fermentation conditions of TS-SSF were based on the experimental optimum of our previous studies.
For GS-SSF, 0.5 g ammonium sulfate/100 g SSS (DM) and 0.5 g calcium chloride/100 g SSS (DM) were added into five different biomass particles and mixed well. The moisture content of SSS was adjusted to 70% by deionized water, and the initial pH was adjusted to 5.0. After heat sterilization at 121°C for 15 min, the mixture was cooled and inoculums of 0.5 g yeast/100 g SSS (DM) were added into the mixture and blended well. As shown in Figure 6, the solid substrate mixtures after sterilization and inoculation were top-loaded into the fermenter through air seal machinery. During ethanol fermentation, the solid substrate mixtures were pushed from the fermenter towards the gas-stripping tank at a predetermined speed by stepping motor. When the solid substrate mixtures reached the gas-stripping tank, ethanol was gas-stripped by CO2 with 10 kg/h at different times. The mixtures of ethanol and CO2 went through an activated carbon adsorption column, and ethanol was absorbed. The absorbed ethanol was desorbed by heating the activated carbon adsorption column and recovered in the receptor by the condensator. The remaining CO2 was recycled, and it was saturated by the humidifier before it was injected into the gas-stripping tank again.
Determination of CO2 weight loss
Release of CO2 during SSF was adopted to evaluate the fermentation power of ethanol production from SSS. The reaction equation for growth of S. cerevisiae on glucose is:
Carbohydrates were converted to CO2 and ethanol. Production of CO2 overflowed from the shake flask caused a decrease in the weight of the fermented substrate, hence the weight of the shake flask reduced. Weight loss of CO2 in fermentation was measured by an accurate balance (0.01 g). It can be measured based on the total weight loss of the shake flask every 2 hours. The CO2 weight loss rate was defined as CO2 weight loss per 2 h.
Analytical methods and calculations
The composition analysis of SSS was conducted according to the Laboratory Analysis Protocol (LAP) of the National Renewable Energy Laboratory (NREL), Golden, CO, USA [43–45]. The moisture content of SSS was determined using oven drying at 105°C for 24 h. The concentrations of sugar and ethanol were analyzed by HPLC (Agilent 1200, Agilent Technologies, Santa Clara, CA, USA), equipped with a refractive index detector and an Aminex HPX-87H carbohydrate analysis column (Bio-Rad, Hercules, CA, USA) at 35°C with 5 mM H2SO4 as the mobile phase at a flow rate of 0.6 mL/min. Sucrose, glucose, fructose, and ethanol standards used in the experiment were analytical grade and were purchased from Sigma-Aldrich (St Louis, MO, USA).
The ethanol yield was used as the key metric for evaluation of SSF performance. Ethanol stripping efficiency was used for determination of the online ethanol separation efficiency in GS-SSF. They were calculated as follows:
Gas stripping solid state fermentation
High performance liquid chromatography
Laboratory Analysis Protocol
National Renewable Energy Laboratory
Solid state fermentation
Sweet sorghum stalk
Traditional static solid state fermentation
Yeast extract peptone dextrose.
Chen HZ, Qiu WH: Key technologies for bioethanol production from lignocelluloses. Biotechnol Adv 2010, 28: 556-562. 10.1016/j.biotechadv.2010.05.005
Harun S, Balan V, Takriff MS, Hassan O, Jahim J, Dale BE: Performance of AFEX™ pretreated rice straw as source of fermentable sugars: the influence of particle size. Biotechnol Biofuels 2013, 6: 40. 10.1186/1754-6834-6-40
Mosier N, Wyman C, Dale BE, Elander R, Lee YY, Holtzapple M, Ladisch M: Features of promising technologies for pretreatment of lignocellulosic biomass. Bioresour Technol 2005, 96: 673-686. 10.1016/j.biortech.2004.06.025
Olofsson K, Bertilsson M, Lidén G: A short review on SSF-an interesting process option for ethanol production from lignocellulosic feedstocks. Biotechnol Biofuels 2008, 1: 7. 10.1186/1754-6834-1-7
Liu ZH, Qin L, Jin MJ, Pang F, Li BZ, Kang Y, Dale BE, Yuan YJ: Evaluation of storage methods for the conversion of corn stover biomass to sugars based on steam explosion pretreatment. Bioresour Technol 2013, 132: 5-15.
Qin L, Liu ZH, Li BZ, Dale BE, Yuan YJ: Mass balance and transformation of corn stover by pretreatment with different dilute organic acids. BioresourTechnol 2012, 112: 319-326.
Petti C, Harman-Ware AE, Tateno M, Kushwaha R, Shearer A, Downie AB, Crocker M, DeBolt S: Sorghum mutant RG displays antithetic leaf shoot lignin accumulation resulting in improved stem saccharification properties. Biotechnol Biofuels 2013, 6: 146. 10.1186/1754-6834-6-146
Wu XR, Staggenborg S, Propheterb JL, Rooney WL, Yu JM, Wang DH: Features of sweet sorghum juice and their performance in ethanol fermentation. Ind Crop Prod 2010, 31: 164-170. 10.1016/j.indcrop.2009.10.006
Yu JL, Zhang X, Tan TW: Ethanol production by solid state fermentation of sweet sorghum using thermotolerant yeast strain. Fuel Process Technol 2008, 89: 1056-1059. 10.1016/j.fuproc.2008.04.008
Martin AP, Palmer WM, Byrt CS, Furbank RT, Grof CPL: A holistic high-throughput screening framework for biofuel feedstock assessment that characterises variations in soluble sugars and cell wall composition in Sorghum bicolor. Biotechnol Biofuels 2013, 6: 186. 10.1186/1754-6834-6-186
Cai H, Dunn JB, Wang ZC, Han J, Wang MQ: Life-cycle energy use and greenhouse gas emissions of production of bioethanol from sorghum in the United States. Biotechnol Biofuels 2013, 6: 141. 10.1186/1754-6834-6-141
Calvinŏ M, Messing J: Sweet sorghum as a model system for bioenergy crops. Curr Opin Biotechnol 2012, 23: 323-329. 10.1016/j.copbio.2011.12.002
Sánchez ÓJ, Cardona CA: Trends in biotechnological production of fuel ethanol from different feedstocks. Bioresour Technol 2008, 99: 5270-5295. 10.1016/j.biortech.2007.11.013
Zhao YL, Dolat A, Steinberger Y, Wang X, Osman A, Xie GH: Biomass yield and changes in chemical composition of sweet sorghum cultivars grown for biofuel. Field Crop Res 2009, 111: 55-64. 10.1016/j.fcr.2008.10.006
Laopaiboon L, Thanonkeo P, Jaisil P, Laopaiboon P: Ethanol production from sweet sorghum juice in batch and fed-batch fermentations by Saccharomyces cerevisiae . World J Microbiol Biotechnol 2007, 23: 1497-1501. 10.1007/s11274-007-9383-x
Li JH, Li SZ, Han B, Yu MH, Li GM, Jiang Y: A novel cost-effective technology to convert sucrose and homocelluloses in sweet sorghum stalks into ethanol. Biotechnol Biofuels 2013, 6: 174. 10.1186/1754-6834-6-174
Pandey A: Solid-state fermentation. Biochem Eng J 2003, 13: 81-84. 10.1016/S1369-703X(02)00121-3
Singhania RR, Patel AK, Soccol CR, Pandey A: Recent advances in solid-state fermentation. Biochem Eng J 2009, 44: 13-18. 10.1016/j.bej.2008.10.019
Singhania RR, Sukumaran RK, Patel AK, Larroche C, Pandey A: Advancement and comparative profiles in the production technologies using solid-state and submerged fermentation for microbial cellulases. Enzyme Microb Technol 2010, 46: 541-549. 10.1016/j.enzmictec.2010.03.010
Chen HZ, Li YJ, Xu FJ: Impact of operating conditions on performance of a novel gas double-dynamic solid-state fermentation bioreactor (GDSFB). Bioprocess Biosyst Eng 2013, 36: 1753-1758. 10.1007/s00449-013-0950-2
He Q, Chen HZ: Pilot-scale gas double-dynamic solid-state fermentation for the production of industrial enzymes. Food Bioprocess Technol 2013, 6: 2916-2924. 10.1007/s11947-012-0956-9
Mitchell DA, Krieger N, Stuart DM, Pandey A: New developments in solid-state fermentation II. Rational approaches to the design, operation and scale-up of bioreactors. Process Biochem 2000, 35: 1211-1225. 10.1016/S0032-9592(00)00157-6
Li SH, Li GM, Zhang L, Zhou ZX, Han B, Hou WH, Wang JB, Li TC: A demonstration study of ethanol production from sweet sorghum stems with advanced solid state fermentation technology. Appl Energ 2013, 102: 260-265.
Kwon YJ, Wang F, Liu CZ: Deep-bed solid state fermentation of sweet sorghum stalk to ethanol by thermotolerant Issatchenkiaorientalis IPE 100. Bioresour Technol 2001, 102: 11262-11265.
Shen F, Liu RH: Research on solid-state ethanol fermentation using dry sweet sorghum stalk particles with active dry yeast. Energ Fuel 2009, 23: 519-525. 10.1021/ef800531e
Moukamnerd C, Kino-oka M, Sugiyama M, Kaneko Y, Boonchird C, Harashima S, Noda H, Ninomiya K, Shioya S, Katakura Y: Ethanol production from biomass by repetitive solid-state fed-batch fermentation with continuous recovery of ethanol. Appl Microbiol Biotechnol 2010, 88: 87-94. 10.1007/s00253-010-2716-y
Couto SR, Sanromán MA: Application of solid-state fermentation to food industry - a review. J Food Eng 2006, 76: 291-302. 10.1016/j.jfoodeng.2005.05.022
Gervais P, Molin P: The role of water in solid-state fermentation. Biochem Eng J 2003, 13: 85-101. 10.1016/S1369-703X(02)00122-5
Jin MJ, Lau MW, Balan V, Dale BE: Two-step SSCF to convert AFEX-treated switchgrass to ethanol using commercial enzymes and Saccharomyces cerevisiae 424A (LNH-ST). Bioresour Technol 2010, 101: 8171-8178. 10.1016/j.biortech.2010.06.026
Liu ZH, Qin L, Pang F, Jin MJ, Li BZ, Kang Y, Dale BE, Yuan YJ: Effects of biomass particle size on steam explosion pretreatment performance for improving the enzyme digestibility of corn stover. Ind Crop Prod 2013, 44: 176-184.
Yu B, Chen HZ: Effect of the ash on enzymatic hydrolysis of steam-exploded rice straw. Bioresour Technol 2010, 23: 9114-9119.
Nagel FJ, Tramper J, Bakker MS, Rinzema A: Model for on-line moisture-content control during solid-state fermentation. Biotechnol Bioeng 2001, 72: 231-243. 10.1002/1097-0290(20000120)72:2<231::AID-BIT11>3.0.CO;2-S
Liu RH, Shen F: Impacts of main factors on bioethanol fermentation from stalk juice of sweet sorghum by immobilized Saccharomyces cerevisiae (CICC 1308). Bioresour Technol 2008, 99: 847-854. 10.1016/j.biortech.2007.01.009
Chen HZ, Li GH: An industrial level system with nonisothermal simultaneous solid state saccharification, fermentation and separation for ethanol production. Biochem Eng J 2013, 74: 121-126.
Jin MJ, Gunawan C, Uppugundla N, Balan V, Dale BE: A novel integrated biological process for cellulosic ethanol production featuring high ethanol productivity, enzyme recycling and yeast cells reuse. Energy Environ Sci 2012, 5: 7168-7175. 10.1039/c2ee03058f
Krishna SH, Reddy TJ, Chowdary GV: Simultaneous saccharification and fermentation of lignocellulosic wastes to ethanol using a thermotolerant yeast. Bioresour Technol 2001, 77: 193-196. 10.1016/S0960-8524(00)00151-6
de Vrije T, Budde M, van der Wal H, Claassen PAM, López-Contreras AM: “In situ” removal of isopropanol, butanol and ethanol from fermentation broth by gas stripping. Bioresour Technol 2013, 137: 153-159.
Couto SR, Sanromán MA: Application of solid-state fermentation to ligninolytic enzyme production. Biochem Eng J 2005, 22: 211-219. 10.1016/j.bej.2004.09.013
Chen HZ, He Q: A novel structured bioreactor for solid-state fermentation. Bioprocess Biosyst Eng 2013, 36: 223-230. 10.1007/s00449-012-0778-1
Pandey A, Soccol CR, Mitchell M: New developments in solid state fermentation: I-bioprocesses and products. Process Biochem 2000, 35: 1153-1169. 10.1016/S0032-9592(00)00152-7
de Castro RJS, Sato HH: Synergistic effects of agro-industrial wastes on simultaneous production of protease and α -amylase under solid state fermentation using a simplex centroid mixture design. Ind Crop Prod 2013, 49: 813-821.
Durand A: Bioreactor designs for solid state fermentation. Biochem Eng J 2003, 13: 113-125. 10.1016/S1369-703X(02)00124-9
Sluiter A, Hames B, Ruiz R, Scarlata C, Sluiter J, Templeton D, Crocker D: Determination of structural carbohydrates and lignin in biomass. . Laboratory Analytic Procedure (LAP) of the National Renewable Energy Laboratory (NREL), Golden, CO, USA. 2008 http://www.nrel.gov/docs/gen/fy13/42618.pdf
Sluiter A, Hames B, Ruiz R, Scarlata C, Sluiter J, Templeton D: Determination of Ash in Biomass. . Laboratory Analytic Procedure (LAP) of the National Renewable Energy Laboratory (NREL), Golden, CO, USA. 2008 http://www.nrel.gov/docs/gen/fy08/42622.pdf
Hames B, Ruiz R, Scarlata C, Sluiter A, Sluiter J, Templeton D: Preparation of Samples for Compositional Analysis. . Laboratory Analytic Procedure (LAP) of the National Renewable Energy Laboratory (NREL), Golden, CO, USA. 2008 http://www.nrel.gov/docs/gen/fy08/42620.pdf
This work was financially supported by the National Basic Research Program of China (973 Project, 2011CB707401), the National High Technology Research and Development Program (863 Program, 2012AA021302), and the Open Funding Project of the National Key Laboratory of Biochemical Engineering (2013KF-01).
The authors declare that they have no competing interests.
CHZ and LZH participated in the design of the study. LZH performed the statistical analysis and drafted the manuscript. LZH and DSH carried out the SSF experiments. LZH revised the manuscript. All authors provided critical input to the manuscript and read and approved the final manuscript.
An erratum to this article is available at http://dx.doi.org/10.1186/s13068-015-0365-1.
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Chen, HZ., Liu, ZH. & Dai, SH. A novel solid state fermentation coupled with gas stripping enhancing the sweet sorghum stalk conversion performance for bioethanol. Biotechnol Biofuels 7, 53 (2014). https://doi.org/10.1186/1754-6834-7-53
- Gas stripping (GS)
- Solid state fermentation (SSF)
- Traditional static solid state fermentation (TS-SSF)
- Sweet sorghum stalk (SSS)
- Particle thickness
- Ethanol stripping efficiency
- Carbon dioxide weight loss
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