Arthur E.
Pastore de Lima
ab,
Russell L.
Wrobel
bc,
Brandon
Paul
ab,
Larry C.
Anthony
d,
Trey K.
Sato
b,
Yaoping
Zhang
b,
Chris Todd
Hittinger
bc and
Christos T.
Maravelias
*ef
aDepartment of Chemical and Biological Engineering, University of Wisconsin–Madison, 1415 Engineering Dr, Madison, WI 53706, USA
bDOE Great Lakes Bioenergy Research Center, University of Wisconsin, 1552 University Avenue, Madison, WI 53726, USA
cLaboratory of Genetics, Wisconsin Energy Institute, J. F. Crow Institute for the Study of Evolution, Center for Genomic Science Innovation, University of Wisconsin–Madison, Madison, WI 53726, USA
dIFF, Health and Biosciences, Wilmington, DE, USA
eDepartment of Chemical and Biological Engineering, Princeton University, Princeton, NJ 08544, USA. E-mail: maravelias@princeton.edu
fAndlinger Center for Energy and the Environment, Princeton University, Princeton, NJ 08544, USA
First published on 23rd June 2023
Biofuels from sustainable feedstocks are a promising option for carbon-neutral bioenergy, where isobutanol has been receiving attention due to its advantageous physical and chemical properties. In this work, the production of isobutanol from carbohydrates in ammonia fiber expansion-pretreated switchgrass hydrolysate is investigated. We engineer a yeast strain by hybridizing an industrial starch isobutanologen with a strain that can tolerate the stresses of lignocellulosic hydrolysates. This strategy increases isobutanol production through ethanol co-production, which enables improved yeast growth and higher metabolic flux under these stressful conditions, likely due to the presence of at least some pyruvate decarboxylase. Furthermore, we develop a process for the recovery of isobutanol and ethanol from the broth and perform technoeconomic analysis of the switchgrass-to-alcohol biorefinery based on experiments. The yeast consumes all available glucose, but no xylose, available in the hydrolysate and co-produces isobutanol and ethanol at 23.7% and 61.8% theoretical yields, respectively. An estimated baseline minimum selling price of $11.41 per GGE for isobutanol and ethanol is determined and sensitivity analysis identified the key parameters affecting the economic feasibility of the process. Specifically, hydrolysis enzyme loading, the sugar concentration in hydrolysate, and potential fermentation technological advances, such as xylose conversion to alcohols, were shown to have the greatest economic impact.
Besides its advantageous properties as a fuel, isobutanol is a suitable precursor for different chemicals, such as ketones,4 isobutyl acetate,5 and isobutene.6 In particular, isobutene is a platform chemical that can be further upgraded to chemicals such as p-xylene,7 methacrolein and methacrylic acid,8 butyl rubber and other polymers,9 isooctane, or other fuel additives, such as tert-butyl ethers.10,11 Furthermore, isobutene can be oligomerized to fuel distillates in the range of jet fuel and diesel.12–15
One of the most important industrial processes for isobutanol production is the hydroformylation of propylene (oxo synthesis).16 Propylene, carbon monoxide, and hydrogen react to produce a mixture of isobutyraldehyde and butyraldehyde, which are hydrogenated to isobutanol and n-butanol, respectively. The feedstock propylene is mainly obtained from fossil-based sources through an energy-intensive process (steam cracking of propane). An alternative means to produce isobutanol is by biological conversion of carbohydrate molecules by microbes.17 Microbial fermentation sustainably converts sugars (e.g., glucose, xylose) obtained from lignocellulosic biomass to biofuels and products.
Lignocellulosic biomass is a low-cost and largely available feedstock option. Furthermore, the use of lignocellulosic biomass avoids the use of food crops for fuel and energy production because lignocellulose does not directly compete with food production.18 For instance, switchgrass is a lignocellulosic biomass crop that can be grown on lands that are not used for food production and requires low nitrogen input.19
Lignocellulosic biomass requires a pretreatment step to increase the yield of fermentable sugars. Biomass pretreatment disrupts the structure of the lignocellulosic material and exposes the carbohydrate polymers, which makes cellulose and hemicellulose more accessible to the enzymes used in the subsequent hydrolysis step.20 Ammonia fiber expansion (AFEX) is a pretreatment that employs ammonia at high temperatures and pressure. The use of ammonia has the advantage of solubilizing lignin, which allows for the fractionation of biomass and increases the efficiency of enzymes during hydrolysis.21 In the hydrolysis step, the enzymes convert the cellulose and hemicellulose into sugars (mainly glucose and xylose). Next, the hydrolysate is sent to fermentation, where it is inoculated with the fermenting microorganisms consuming sugars to produce alcohols.22,23 To overcome the low tolerance of microorganisms to isobutanol, in situ product removal methods are required to reduce isobutanol concentration. The most promising techniques are vacuum evaporation, adsorption, pervaporation, gas stripping, and solvent extraction.24
Isobutanol is naturally produced via the Ehrlich pathway at low mg L−1 titers from amino acid degradation by native yeast strains, such as Saccharomyces cerevisiae,25 whereas many microorganisms typically cannot produce appreciable isobutanol natively.26 Microbial engineering has been extensively applied to enhance isobutanol production and increase the yields and titers obtained by different microorganisms, such as S. cerevisiae,27–30Escherichia coli,31–33 and many others.34–43
Different feedstocks have been used to produce isobutanol using these microorganisms. Atsumi et al. engineered E. coli bacteria to produce 22 g L−1 of isobutanol from glucose.32 Jung et al. produced 23 g L−1 of isobutanol using engineered Enterobacter aerogenes from sugarcane bagasse.42 Switchgrass39 and cellulose37 were used to produce 0.66 g L−1 by Caldicellulosiruptor bescii and 0.17 g L−1 of isobutanol by Clostridium cellulolyticum, respectively, with no hydrolysis step. Other works focused on the consumption of hemicellulose fraction by bacterium40 and xylose by yeast29,44,45 to produce isobutanol, albeit at low titers and yields. Nakashima and Tamura were able to produce 11 g L−1 of isobutanol by E. coli using a medium with a mixture of glucose and xylose.46 Note that in some systems, by-products, such as ethanol,43 2-methyl-1-butanol,29 hexanol,39 lactate, succinate,47 and others, are produced.
To assess the economic feasibility of new processes and microorganisms used for isobutanol production in lignocellulosic biorefineries, analyses based on experimental data must be carried out. Technoeconomic analysis of isobutanol production system has been conducted by a few authors.3,48,49 Tao et al. reported an isobutanol minimum fuel selling price (MFSP) of $3.62 per gasoline gallon equivalent (GGE) using corn stover as feedstock; they considered isobutanol yields from glucose and xylose of 85% of the theoretical maximum and performed sensitivity analysis.49 Roussos et al. determined an MFSP of $6.53 per GGE ($4.14 per GGE) for isobutanol using corn stover as feedstock and assuming yields of 85% (90%) of the theoretical maximum from glucose and xylose,3 which are based on the work of Tao et al.49 Note that the high xylose-to-isobutanol yields used in these works were not verified experimentally; it was assumed that xylose is converted at yields comparable to glucose. Furthermore, these works did not consider the co-production of isobutanol and other (by-)products.
In summary, many experimental works have focused on engineering microbes to produce isobutanol from different substrates. Obtaining high-yield fermentation data from lignocellulosic biomass hydrolysate is still a challenge due to the inhibitory components in the hydrolysates; the toxicity of the isobutanol product itself on microorganisms; metabolic barriers that limit biofuel titer, rate, and yield; and high water content in the broth.24 However, producing isobutanol at high yields using lignocellulosic biomass and identifying areas of improvement are necessary to obtain an economically competitive biomass-based isobutanol. The contribution of this work is three-fold. First, we demonstrate the high-yield co-production of isobutanol and ethanol from AFEX-pretreated switchgrass hydrolysate (ASGH) by a hybrid triploid yeast strain. The isobutanologen co-produces ethanol to enable growth and metabolic flux under these stressful conditions. Second, we synthesize a switchgrass-to-alcohol biorefinery with emphasis on the separations necessary to obtain isobutanol and ethanol from the fermentation broth. Finally, we perform a technoeconomic analysis based on experimental results, thus providing an economic assessment for isobutanol and ethanol co-production in an integrated pipeline using our hybrid yeast strain. We provide further insights into the impact of potential process and fermentation strain improvements on the economics of the system using sensitivity analysis.
The major extracellular end-products obtained from the anaerobic fermentation of ASGH by yHRW253 are ethanol, isobutanol, and glycerol. The ASGH contains 56.6 g L−1 glucose and 39.7 g L−1 xylose (see Section 5.2). Table 1 shows the titer and yield from glucose for these products. Glucose is completely consumed, while xylose remains unconverted. The yield of alcohols from glucose is 85.5% ± 0.9% of the theoretical maximum, and the ratio of ethanol/isobutanol produced is 3.24 ± 0.05.
Product | Titer (g L−1) | Yield (% of theoretical maximum)a |
---|---|---|
a The theoretical yield of isobutanol (ethanol) is 0.41 (0.51) g g−1 of glucose. Results based on initial glucose concentration of 56.6 g L−1 and xylose concentration of 39.7 g L−1. b NC: not calculated. | ||
Isobutanol | 5.52 ± 0.04 | 23.7% ± 0.2% |
Ethanol | 17.87 ± 0.25 | 61.8% ± 0.9% |
Glycerol | 5.13 ± 0.17 | NCb |
Each block in the process (see Fig. 1) consists of multiple unit operations and is characterized by cost, energy demand (i.e., heat and electricity), and conversion parameters. The baseline parameter values of the AFEX and HYD blocks are calculated from the literature23,52–56 after adjustments to account for the values of experimental operating parameters used in this work (e.g., NH3/dry biomass ratio and enzyme loading – see Sections 5.2 to 5.4). The parameter values for FILT, WWT, CB, and TBG blocks are estimated from the literature.23,55,56
A process simulation for the FERM and SEP blocks is developed in Aspen Plus V11 process simulator (Aspen Technology Inc.). The SEP block uses multiple distillation columns at different pressures, similar to systems such as the acetone–butanol–ethanol separation process,51 to recover most of the isobutanol and ethanol from the broth (see Section 5.5 for details). The process simulation results are used to estimate the parameters of the process optimization model for the FERM and SEP blocks (e.g., cost and energy parameters). The isobutanol and ethanol recoveries for the baseline design are 99.5% and 97.3%, respectively. The values of estimated parameters are given in the ESI.†
To synthesize the biorefinery, we use an optimization model55,56 that includes material and energy balances across all the major blocks of the biorefinery (e.g., AFEX, HYD, FERM). We minimize the cost to produce one kg of alcohol (isobutanol + ethanol). The complete mathematical formulation is detailed in the ESI.† The switchgrass is assumed to consist of 34.1% of cellulose, 27.0% of hemicellulose, and 26.4% of lignin, and it is available at $101 Mg−1.57 The ratio of isobutanol to ethanol produced is 0.315 kg of isobutanol per kg of ethanol, and the resulting alcohol yield is 0.111 kg of alcohol per kg of switchgrass (Fig. 1).
Fig. 2 Cost contributions in the baseline biorefinery. The MFSP is $11.41 per gasoline gallon equivalent (GGE). |
The total estimated heat and electricity demand of the process are 15.4 and 4.9 kW h kg−1 of alcohol (isobutanol + ethanol), respectively, whereas a revenue of $2.51 per GGE is obtained from the electricity surplus sold to the grid. Most of the heat is used by the SEP (59% of total heat demand) and AFEX (34.1%) blocks, while electricity is required mostly in the HYD (57.8%) and WWT (21.5%) blocks.
Fig. 3 (a) Change in the minimum fuel selling price (ΔMFSP) for each case. The baseline MFPS is $11.41 per GGE. (b) Cost contributions in the switchgrass-to-alcohol biorefinery for cases (A) to (F). |
In case (A), a 25% reduction in the switchgrass price (from $101 Mg−1 to $76 Mg−1) reduces the feedstock cost contribution by $0.96 per GGE, representing a 8.4% MFSP decrease. In case (B), the AFEX residence time is reduced from 30 to 15 min (50%), affecting the capital and fixed operating costs, and resulting in savings of $0.29 per GGE (2.6%). In case (C), the mass ratio of NH3/dry biomass loaded in the AFEX reactor is reduced from 1.0 to 0.5 (50%), which affects the make-up flow of ammonia, the energy demand, and the capital costs of AFEX. The MFSP is reduced by $0.75 per GGE (6.6%), due to cost savings of $0.22 per GGE and an additional $0.54 per GGE in electricity surplus revenue.
In our analysis, we assumed that hydrolysis enzymes are produced on-site23 and that the cost and energy demand associated with enzyme production scales with enzyme loading. In case (D), the enzyme loading is reduced from 93 to 46.5 mg protein per g glucan (50% reduction), decreasing the MFSP by $2.48 per GGE (21.7%). The improvement comes from a significant reduction in HYD costs ($2.13 per GGE) and additional electricity surplus revenue ($0.35 per GGE).
In case (E), we consider a higher sugar concentration in the hydrolysate, while maintaining the same glucose/xylose ratio. The sugar concentration is increased by 50%, from 96.3 g L−1 to 144.5 g L−1 (84.9 g L−1 of glucose and 59.6 g L−1 of xylose). The cost and energy demand parameters of the FERM and SEP blocks are re-estimated using process simulation based on the new sugar concentration. The MFSP decreases by $1.38 per GGE (12.1%) due to cost savings ($0.66 per GGE) and additional electricity surplus revenue ($0.72 per GGE).
In case (F), we consider that the yeast would be capable of converting xylose to isobutanol and ethanol (e.g., through further engineering of yHRW253), achieving half the glucose yields (i.e., the yields to isobutanol and ethanol from xylose are 11.8% and 30.9% of the theoretical maximum, respectively). As before, the cost and energy demand parameters for the FERM and SEP blocks are re-calculated. The MFSP decreases by $2.14 per GGE (18.7%). Note that revenues from electricity surplus are reduced by 67%, representing $1.69 per GGE of lost revenue compared to the baseline design; however, cost savings of $3.83 per GGE are achieved by all blocks throughout the biorefinery.
Finally, we perform sensitivity analysis considering multiple changes simultaneously. First, we consider simultaneous improvements in the AFEX and HYD bocks, combining cases (B), (C), and (D). Second, we consider improvements in switchgrass purchasing cost and the FERM block, combining cases (A), (E), and (F). Finally, we consider all improvements, (A) through (F), simultaneously. The change in MFSP and cost contributions for the combined cases are shown in Fig. 4.
Fig. 4 (a) Change in MFSP based on multiple improvements. (b) Cost contributions in the switchgrass-to-alcohol biorefinery for scenarios with multiple improvements. |
The improvements in AFEX and HYD, cases (B)–(D), reduce the MFSP by $3.45 per GGE (30.3%); electricity revenue increases by $0.89 per GGE and costs decrease by $2.56 per GGE, mainly in the AFEX and HYD blocks. The improvements in FERM combined with switchgrass cost reduction, cases (A), (E), and (F), decrease the MFSP by $3.95 per GGE (34.6%), where $1.16 per GGE of electricity surplus revenue is lost due to reduced heat production from biogas, but cost reductions amount to $5.11 per GGE.
Finally, the combination of all improvements considered in this work results in an MFSP of $4.94 per GGE (a reduction of $6.47 per GGE compared to the baseline design). The reduction in the MFSP is mainly due to cost savings ($6.97 per GGE), whereas the electricity surplus revenue drops by $0.51 per GGE.
We consider improvements in the AFEX and HYD blocks by reducing the NH3/dry biomass mass ratio, the AFEX residence time, and the enzyme loading by 50% compared to the baseline design. Note that similar, and even more optimistic, improvements have been considered in other works. For example, Teymouri et al. reported an optimal AFEX residence time of 5 min (83.3% lower compared to this work) for corn stover pretreatment.59 Humbird et al. considered an enzyme loading of 20 mg of protein per g of glucan in a biorefinery for bioethanol production (i.e., 78.5% lower).23 Our results show that the MFSP can be reduced by $3.45 per GGE with the 50% improvements considered in the AFEX and HYD. Therefore, a lower NH3/biomass ratio in AFEX pretreatment and lower enzyme loading in HYD can lead to improved process economics.
The sensitivity analysis shows that the sugar concentration in the hydrolysate and the ability to convert xylose to alcohols are important drivers of the MFSP. Higher sugar concentration in the hydrolysate reduces the volume of broth required to be processed (to produce a fixed amount of alcohol), thereby reducing the size of equipment required in FERM and SEP blocks and generating less volume of wastewater to be treated; it also decreases the heat required in the SEP block, increasing the surplus of electricity sold to the grid (Fig. 3b).
The fermentation of xylose reduces the unit costs ($ per kg of alcohol) of all biorefinery blocks due to higher product yields (Fig. 3b). In case (F), and combined cases [(A), (E) and (F)] and [(A)–(F)], the conversion of xylose to alcohols results in smaller sugar amounts (and switchgrass, consequently) required to produce the same amount of alcohol, thereby reducing the flows and unit costs throughout the biorefinery. Note that unconverted xylose generates biogas in the WWT block (Fig. 1), resulting in a significant decrease in electricity surplus once a fraction of xylose is converted to alcohols in FERM (Fig. 3b). Therefore, further engineering of yeast yHRW253 towards xylose fermentation to increase product yields will result in significant cost reduction.
Note that both sugar concentration in hydrolysate and xylose conversion affect the concentration of isobutanol in the broth. In the sensitivity analysis, we assumed that microorganisms would not be significantly affected by the higher isobutanol concentration compared to the baseline design. This assumption may not hold at higher isobutanol yields, but strategies to remove isobutanol-rich vapors directly from the broth (e.g., vacuum stripping) could address this potential limitation.
Finally, we note that other improvements, not considered herein (e.g., the use of simultaneous saccharification and fermentation) could also lead to better process economics.
We synthesize a switchgrass-to-alcohol biorefinery using the yHRW253 hybrid strain for isobutanol and ethanol co-production for $11.41 per GGE. Cost analysis of the baseline design shows that the major biorefinery costs are HYD operation followed by switchgrass purchasing. Furthermore, we identify critical parameters that impact the economic feasibility of the proposed biorefinery. Our results suggest that the effect of lower NH3/biomass mass ratio during AFEX pretreatment and lower enzyme loading during HYD should be studied to ensure high sugar yields, while avoiding large economic burdens to the biorefinery. In addition, further research focused on converting the available xylose to alcohols is critical to reducing the switchgrass cost contribution and obtaining a more economically competitive biorefinery.
The industrial isobutanologen BTX1858 was obtained from Butamax Advanced Biofuels LLC, under a Material Transfer Agreement. The BTX1858 strain produces isobutanol as a single alcohol at high yield. The GLBRCY945 and BTX1858 strains were transformed with the HyPr plasmids pHRW34 and pHCT2, respectively, and mating was induced as described previously.61,62 Hybrids were selected YPD plates containing 100 mg mL−1 of both nourseothricin and zeocin. The HyPr plasmids were cured from the triploid hybrid by growing for multiple generations in non-selective liquid media. The yHRW253 hybrid was verified by the PCR amplification of the polymorphic loci FLO8, GRE3, and HOG1.
The bioreactor fermentations in Tables S1–S3† were conducted for 48 hours in 250 mL Minibio bioreactors (Applikon Biotechnology, Foster City, CA) containing 100 mL of ASGH or production medium (1.7 g L−1 Difco Yeast Nitrogen Base without Amino Acids and Ammonium Sulfate, 5 g L−1 ammonium sulfate, 1 g L−1 yeast extract, 60 g L−1 dextrose, 2 mL L−1 1:100 diluted Antifoam 204, 3 mL L−1 nicotinic acid (10 mg mL−1 stock), 3 mL L−1 thiamine (10 mg mL−1 stock), 0.8 g L−1 KH2PO4, 1.9 g L−1 K2HPO4, pH 5.2, 0.2 μm filter-sterilized). Prior to fermentation, ASGH was adjusted to pH 5.8 using 10 N NaOH and filtered through a 0.2 μm filter to remove precipitates and ensure sterility. Overnight aerobic-grown starter cultures of Y945 in YPD (10 g L−1 yeast extract, 20 g L−1 peptone, 20 g L−1 dextrose) and BTX1858 in SD (19.5 g L−1 MES, 1.7 g L−1 Difco Yeast Nitrogen Base without Amino Acids and Ammonium Sulfate, 5 g L−1 ammonium sulfate, 1.7 g L−1 yeast drop-out mix without uracil, 3 g L−1 glucose, pH 5.5 using 5% KOH, 0.2 μm filter-sterilized) were centrifuged at 14000g for 3 minutes, and the supernatants were discarded. The cell pellets were resuspended into 5 mL of ASGH or production medium from each vessel, and the suspensions were then inoculated back into each vessel to give each an initial OD600 of 0.5. Fermentation was conducted at 30 °C with continuous stirring (500 rpm), pH was controlled at 5.8, and samples were removed from the bioreactors for an OD600 measurement to monitor cell growth and for HPLC-RID and GC/MS to measure the concentrations of glucose, xylose, and the end products as described previously.27 Percent theoretical yields were calculated using the amount of glucose (and xylose for GLBRCY945) consumed.
The cost and energy demand parameters for the AFEX block are adapted from the literature52 after adjusting for the NH3/dry biomass mass ratio and residence time used in this study (see Section 5.2). The cost and energy demand parameters of the HYD block are estimated from NREL reports53,54 and include on-site enzyme production,23 which is scaled based on the enzyme loading of this study. Linear scaling is used for material and energy flows, while power-law scaling (exponent of 2/3) is used for capital costs. We estimate the cost and energy demand parameters for the FERM and SEP blocks using detailed process simulations (Section 5.5) due to the dependence of these parameters on the product yields and ASGH sugar concentration. The parameters for FILT, WWT, CB, and TBG blocks are estimated from the literature.23,55,56 The list of used parameter values is detailed in the ESI.†
A total of 402 m3 h−1 of hydrolysate is processed in 12 parallel bioreactors (each processing 33.5 m3 h−1 of hydrolysate). Since the titer of isobutanol in the fermentation broth is relatively low (see Section 2.2), we consider that the concentration of isobutanol in the broth does not reach toxic levels. The broth is sent to the beer column (COL-101) operated at 150 kPa. Solids and the stillage containing large amounts of water are removed at the bottom, while the distillate, containing isobutanol, ethanol, and water, is sent to a vacuum distillation column (COL-102) operated at 30 kPa. The objective of column COL-102 (and COL-103) is to concentrate and recover most of the ethanol in the distillate stream. The distillate in COL-103 is close to the water–ethanol azeotrope, so molecular sieves (M-503) are used to dehydrate the ethanol to 99.5 wt%.23 The bottom streams from COL-102 and COL-103 are rich in water and isobutanol, which form a heteroazeotrope. The streams are sent to a decanter to obtain two liquid phases. The water-rich phase is sent to COL-202, where water is removed at the bottom with minimal loss of isobutanol, and the distillate is recycled to the decanter. The isobutanol-rich phase is purified in COL-201 to obtain 99.5 wt% isobutanol at the bottom, and the distillate, which contains water and isobutanol, is recycled to the decanter. The details of the economic assumptions and cost and energy demand estimates are given in the ESI.†
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d2se01741e |
This journal is © The Royal Society of Chemistry 2023 |