Analysis of alkali ultrasonication pretreatment in bioethanol production from cotton gin trash using FT-IR spectroscopy and principal component analysis
© Placido and Capareda; licensee Springer. 2014
Received: 16 May 2014
Accepted: 22 October 2014
Published: 5 December 2014
Cotton gin trash (CGT) is a lignocellulosic residue that can be used in the production of cellulosic ethanol. In a previous research, the sequential use of ultrasonication, liquid hot water, and ligninolytic enzymes was selected as pretreatment for the production of ethanol from CGT. However, an increment in the ethanol production is necessary. To accomplish that, this research evaluated the effect of pretreating CGT using alkaline ultrasonication before a liquid hot water and ligninolytic enzymes pretreatments for ethanol production. Three NaOH concentrations (5%, 10%, and 15%) were employed for the alkaline ultrasonication. Additionally, this work is one of the first applications of Fourier transform infrared (FT-IR) spectrum and principal component analysis (PCA) as fast methodology to identify the differences in the biomass after different types of pretreatments.
The three concentrations employed for the alkaline ultrasonication pretreatment produced ethanol yields and cellulose conversions higher than the experiment without NaOH. Furthermore, 15% NaOH concentration achieved twofold increment yield versus the treatment without NaOH. The FT-IR spectrum confirmed modifications in the CGT structure in the different pretreatments. PCA was helpful to determine differences between the pretreated and un-pretreated biomass and to evaluate how the CGT structure changed after each treatment.
The combination of alkali ultrasonication hydrolysis, liquid hot water, and ligninolytic enzymes using 15% of NaOH improved 35% the ethanol yield compared with the original treatment. Additionally, we demonstrated the use of PCA to identify the modifications in the biomass structure after different types of pretreatments and conditions.
KeywordsAlkali-hydrolysis Cotton gin trash Ethanol production FT-IR Ligninolytic enzymes Principal components analysis Ultrasonication
Cotton is one of the major crops grown in the world. In 2006 to 2007, the worldwide production was 24 million tons and it continues to increase by 2% each year . The residues from cotton production are of two types: cotton plant trash (CPT) and cotton gin trash (CGT) . CPT is the residue that stays in the field after the harvest of cotton; while CGT is the residue coming from the ginning process. CGT is composed of pieces of sticks, leaves, bolls, and soil cleaned from lint during ginning. In fact, 218 kg of cotton generates 68 to 91 kg of CGT . Annually, the production of this waste in the USA is around 2.26 million tons .
The United States regulation requires by 2020 the production of 36 billion gallons of biofuels and from these, 21 billion should be produced from lignocellulosic materials or other new advanced fuels . Agro-industrial waste (i.e., CGT) is one of the most significant sources of lignocellulosic materials, and bio-ethanol is one of the most essential bio-fuels produced from this kind of wastes. In general, bio-ethanol production from lignocellulosic material includes three principal steps: 1) pretreatment, 2) saccharification, and 3) fermentation. To produce bioethanol from agro-industrial feedstocks, different kinds of pretreatments have been investigated. These are generally divided into physical, physicochemical, chemical, and biological . In CGT, the pretreatment principally used is physicochemical (steam explosion) followed by chemical (acid or basic hydrolysis) and biological (fungal or enzymatic) pretreatment ,. Current biomass pretreatment process utilizes energy intense methodologies (high pressures and temperatures) and harsh chemical compounds.
To overcome the issues related with the traditional pretreatment process, new pretreatment strategies have been evaluated and developed. One of these strategies is the combination of ultrasonication, liquid hot water, and ligninolytic enzymes . The ultrasonication and liquid hot water modified the lignin and cellulose structure; meanwhile, the ligninolytic enzymes treatment realized a detoxification and delignification process. This combination generated an ethanol yield of 30% and cellulose conversion of 23% ; however, both results need to be increased. Cellulose conversion and ethanol yield can be improved by modifying the pretreatment's conditions. Several works proved the efficiency of basic hydrolysis to decrease the lignin content in biomass . Additionally, in sweet sorghum bagasse, the combination of alkaline hydrolysis simultaneously with ultrasonication augmented the final ethanol yield and cellulose conversion . The use of ultrasonication and alkali-hydrolysis has not been tested in CGT; thus, the synergic effect of these technologies may raise delignification, cellulose conversion, and ethanol yield from CGT. The effect of these pretreatments over the CGT structure can be determined using compositional analysis  and/or the biomass' Fourier transform infrared (FT-IR) spectrum. In this moment, FT-IR is principally applied to study qualitatively the modifications in the structure and is not utilized for quantitative analysis. However, FT-IR is a fastest technique compared with the traditional compositional examination and can be used as a tool to identify qualitatively modification in biomass structure after different pretreatments. As a complementary tool to FT-IR spectroscopy, multivariate statistical techniques have been employed to identify the modifications in the FT-IR spectra and evaluate the difference between the different treatments. One of these multivariate methods is the principal component analysis (PCA); this technique reduces the dimensionality of the data by explaining the variance-covariance structure of a set of variables using few linear combinations of these variables. The use of PCA facilitates the visualization of the spectra changes and the identification of the most important features of the FT-IR spectra as the peak shifts and non-symmetries . The use of FT-IR coupled with PCA in pretreated and un-pretreated CGT has not been evaluated in any other research. In the future, this type of methodology can be applied in quality or process control, and if it is coupled with regression techniques, it can be useful to make quantitative evaluations of the biomass composition.
This research evaluated the application of alkali ultrasonication pretreatment as a methodology to increase the ethanol yield produced from CGT using the combination of ultrasonication, liquid hot water, and ligninolytic enzyme. Additionally, FT-IR and PCA were utilized as a tool to analyze the modifications in the biomass structure after pretreatment methodologies.
The samples of CGT were obtained from the Varisco-Court Gin CO near College Station, in Brazos Valley County, Texas. The CGT samples were ground in a Wiley mill (Philadelphia, PA, USA) to achieve an average particle size of approximately 1 mm in diameter.
Pretreatments evaluated in the experiment
Ultrasonication + liquid hot water + ligninolytic enzymes
Ultrasonication/NaOH5% + liquid hot water + ligninolytic enzymes
Ultrasonication/NaOH10% + liquid hot water + ligninolytic enzymes
Ultrasonication/NaOH15% + liquid hot water + ligninolytic enzymes
The saccharification process employed the combination of two types of commercial cellulases: Accellerase 1500 and Accellerase XY (GENENCOR, Palo Alto, CA, USA). The experiment had an initial enzyme loading of 0.3 ml/g of Accellerase 1,500 + 0.1 ml/g of Accellerase XY. The process utilized three replicates in 250-ml Erlenmeyer flasks with 50 ml of a solution of 50-mM sodium acetate buffer at pH 4.8 for 96 h at 50°C and 125 rpm in an incubator/shaker (Innova, New Brunswick Scientific, NJ, USA). Cellulose conversion was calculated by using the next equation: % glucose conversion = [(c × V)/m] × 100 %, where c is the concentration (g/L) of sugars in the sample hydrolyzed, as determined by high performance liquid chromatography (HPLC), V is the total volume (L) hydrolyzed, and m is the initial weight (g) of glucose or xylose determined through the National Renewable Energy Laboratory (NREL) protocols. The statistical tests were performed in the software SAS system 9.3.
Ethanol Red (Saccharomyces cerevisiae) provided by Fermentis (Lesaffre Yeast Corp., Milwaukee, WI, USA) was employed for the fermentation process. The activation of the strain was in 0.5 g of dry yeast in 10 mL of the inoculum broth. The composition of the inoculum broth had 0.2 g glucose, 0.05 g peptone, 0.03 g yeast extracts, 0.01 g KH2PO4, and 0.005 g MgSO4·7H2O. The inoculums were shaken at 200 rpm in an incubator shaker at 38°C for 25 to 30 min. The fermentation process was performed in 125-ml Erlenmeyer flasks with 50 ml of the slurry supplemented with 0.3 g of yeast extract. The slurry was then incubated with 1 ml of freshly activated dry yeast (Ethanol Red) and run for a period of 72 h at 32°C, pH 4, and 100 rpm. The ethanol yield was calculated from the ratio between the average produced ethanol and the theoretical ethanol production of 51.1 g of ethanol generated per 100 g of glucose in the biochemical conversion of the sugar. The response variable was the ethanol yield, and it was analyzed using the software SAS system 9.3 employing one-way ANOVA and the LSD test.
High-performance liquid chromatography
After each of the processes (saccharification and fermentation), the samples were centrifuged at 10,000 rpm for 10 min, and the supernatants were filtered through 0.45-μm hydrophilic PTFE syringe filters (Millipore, Billerica, MA, USA). These samples were then analyzed for glucose, mannose, xylose, arabinose, galactose, and cellobiose concentration using HPLC (Waters 2690, Separations Module, Waters Corporation, Milford, MA, USA) equipped with an auto-sampler, Shodex SP 810 (Shodex, New York, NY, USA) packed column, and a refractive index (RI) detector. Each sample ran for 25 min at a flow rate of 1 ml/min, 60°C using HPLC water as mobile phase.
Wavenumbers of IR vibration frequencies used for CGT characterization
Wave number (cm-1)
C-O-C anti-symmetric stretch (b-1,4 glycosyl)
1,170 to 1,150
Cellulose II and amorphous cellulose strong broad band
Phenolic OH region and aliphatic CH stretch
Aromatic skeletal vibration and CH deformation
Ester carbonyls, C = O
Results and discussion
LSD’s test for the cellulose conversion and ethanol yield
U-NaOH 15% + HW + E
0.409 ± 0.059
U-NaOH 15% + HW + E
0.639 ± 0.139
U-NaOH 10% + HW + E
0.363 ± 0.050
U-NaOH 10% + HW + E
0.585 ± 0.0563
U-NaOH 5% + HW + E
0.329 ± 0.061
U-NaOH 5% + HW + E
0.514 ± 0.077
U + HW + E
0.226 ± 0.056
U + HW + E
0.28867 ± 0.086
0.042 ± 0.002
0.08000 ± 0.104
The cellulose conversion using alkali ultrasonication on CGT (40%) was larger than the conversion found by Silverstein et al.  in cotton stalks (21%) but it was lower than Kaur et al.  over cotton stalks (63%) and Jeihanipour and Taherzadeh  in textiles wastes (99%). The difference between CGT and textile wastes is associated with their composition. Textile wastes comprise small lignin content which allows an easy access to the cellulose. Alkali hydrolysis has been utilized in several types of biomass (sugarcane bagasse, sweet sorghum bagasse, corn stover, etc.) to reduce the lignin content . This pretreatment is normally related with the removal of lignin because NaOH breaks the ester bonds cross-linkage in lignin and xylan . This breaking augments the biomass porosity allowing an easier access of the enzymes to the cellulose. However, alkali hydrolysis normally does not produce considerable modification in the cellulose structure, and this type of modification is necessary to increase the cellulose conversion . The combination of alkaline pretreatment and ultrasonication have been evaluated in sugarcane bagasse and rice straw. In sugarcane, alkali ultrasonication boosted the cellulose conversion approximately 50% against the un-pretreated biomass and 40% versus the pretreatment without ultrasonication . The difference between the pretreated and un-pretreated biomass coincides with the results of this research (Figure 1). In rice straw, the alkali ultrasonication exhibited cellulose conversion greater than the un-pretreated biomass and the alkali pretreatment; nevertheless, the difference between the alkali pretreatment and the alkali ultrasonication was small . The cellulose conversion can be enhanced by different strategies such optimizing the severity of the liquid hot water pretreatment or improving the conditions of the ligninolytic enzymes and ultrasonication pretreatment (reaction time, temperatures, etc.).
The U-NaOH 15% + HW + E's ethanol yield was higher than the yield reported by Shen and Agblevor  on a mix of CGT and recycled paper sludge (40%). Additionally, our results are comparable with the ones described for CGT using steam explosion and a severity of 3.47 (58.1%) . However, the ethanol yield of this research exhibited low values compared with the yields described by Jeoh and Agblevor  and Agblevor et al.  in CGT with conversions around 78% to 95% . The increment in the ethanol yield using NaOH and ultrasonication has been found in other feedstock such as hazelnut husks , cotton stalk , and sugar cane bagasse . The ethanol yields produced in sugar cane bagasse (81%) and hazelnut husks (76.7%) were higher than the U-NaOH 15% + HW + E pretreatment (63%); meanwhile, the alkali-ultrasonicated cotton stalk had an ethanol yield (41%)  that is lower than the pretreatment combination selected in this research.
Structural composition of untreated and pretreated cotton gin trash (CGT)
U + HW + E
U-NaOH 5% + HW + E
U-NaOH 10% + HW + E
U-NaOH 15% + HW + E
Water and ethanol extractives
Acid insoluble material
The absorbance in the cellulose's peaks (898, 1,030, 1,050, 1,090, and 1,170 to 1,150 cm-1) increased at the end of the four experiments. The highest increment in all the pretreatments was the 1,090 cm-1 peak followed by the signals at 898, 1,030, and 1,050 cm-1. U-NaOH 15% + HW + E (Figure 3) obtained the highest increment among the treatments in all the cellulose picks followed by U-NaOH 10% + HW + E pretreatment. The absorbance in the cellulose's signal was increasing according to the pretreatments that were added, showing a synergic effect of the pretreatments over the cellulose structure. In addition to the cellulose peak analysis, the cellulose total crystallinity index (TCI) was utilized to evaluate deeper the cellulose structure. The TCI has been used to express the relative amount of crystalline material in cellulose, and it can be defined using the FT-IR using the absorbance at A1430/A898 . At the end of the four trials, the TCI decreased in 46%, 63%, 66%, and 67% for the pretreatments U + HW + E, U-NaOH 5% + HW + E, U-NaOH 10% + HW + E, and U-NaOH 15% + HW + E, respectively. The reduction in the TCI coincides with the final results observed in the ethanol yield (Figure 2). The decrease in the TCI after alkaline ultrasonication pretreatment was also noticed in the work of Goshadrou et al.  over sweet sorghum bagasse, but in sorghum the shrinkage was lower (13%) than CGT 67%.
In the fully pretreated biomass, the absorbance in the lignin signals (1,370, 1,514, and 1,595 cm-1) reduced compared with the un-pretreated biomass. The hemicellulose signals (1,240 and 1,732 cm-1) obtained the greatest variation among the four experiments evaluated. In these peaks, U + HW + E and U-NaOH 15% + HW incremented the values; meanwhile, U-NaOH 10% + HW + E and U-NaOH 5% + HW reduced the absorbances. These differences can be attributed to the CGT composition and the pretreatment interactions. The increment in the cellulose peak, the diminution in the crystallinity index, and lignin content are some of the reasons why this pretreatment combination produced the greatest cellulose yield and ethanol conversion. The peaks of 898 and 1,030 cm-1 displayed a considerable drop compared with the pretreated biomass; meanwhile, the other peaks did not show any significant change. These differences can be used to follow the hydrolysis reaction of CGT biomass using the FT-IR.
Principal component analysis of the FT-IR spectrum
The cellulose signals found in the loading plots were the signals at 898 (Β-D-cellulose), 1,030, and 1,050 (intense polysaccharide), and 1,090 cm-1 (cellulose II and amorphous cellulose) ,. These points were perceived in PRIN1 and PRIN2 loading plots; in PRIN1, 898 and 1,090 cm-1 were minimums, while 1,030 and 1,050 cm-1 were maximums, which is an opposite behavior compared with PRIN2. These signals showed large values in the PRIN2 than PRIN1, which represents the importance of PRIN2 for the cellulose signals explanation. The most significant lignin signal in the loading plots was the signal at 1,514 cm-1 which is related with the aromatic skeletal vibration and CH deformation. In the same way, the most influential hemicellulose signal in the loading plot was the 1,732 cm-1, this signal was a minimum in both cases and relates the modifications in the esters found in the hemicellulose.
In this research, the addition of alkali ultrasonication pretreatment to liquid hot water and ligninolytic enzyme pretreatments increased the cellulose conversion in 11% to 18% and the ethanol yield in 23% to 35% versus the treatment without alkali ultrasonication. From these pretreatments, the U-NaOH 15% + HW + E pretreatment exhibited the highest cellulose conversion (41%) and ethanol yield (64%). The use of FT-IR and principal components was effective as a tool to identify the variations in the signal of the cellulose, hemicellulose, and lignin from CGT after the different pretreatments. Additionally, the PCA could separate and identify the CGT biomass from different types of pretreatments and identify the signals with the most significant variation inside the spectra. In the future, this type of discrimination technique can be used in the bioethanol industry for quality control and prediction analysis.
The Colombian government and the Fulbright Association are acknowledged for the financial support via the granting of FULBRIGHT-COLCIENCIAS for the PHD studies of Jersson Plácido in the USA. Dr. Raghupathy Karthikeyan and the Water Quality Engineering laboratory are acknowledged for their technical and methodological support as well as the BioEnergy Testing and Analysis Laboratory at the Biological and Agricultural Engineering Department and the Texas AgriLife Research of Texas A&M University for funding this research. GENENCOR International is acknowledged for providing the enzymes employed in the study.
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