ISSN : 0970 - 020X, ONLINE ISSN : 2231-5039
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Investigation of the Effects of Ionic Liquids Pretreatments and Enzymatic Hydrolysis of Kempas, Koompassia malaccensis

Poh Lee Loh, Nur Hasyareeda Hassan* and Muhammad Rahimi Yusop

School of Chemical Sciences and Food Technology, Faculty of Science and Technology, Universiti Kebangsaan Malaysia, 43000 Bangi, Selangor, Malaysia

DOI : http://dx.doi.org/10.13005/ojc/300411

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Article Published : 24 Nov 2014
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ABSTRACT:

The aim of this study is to investigate ionic liquids (ILs) pretreatment on kempas composition, structure and enzymatic digestibility. Ground kempas (Koompassia malaccensis) was pretreated with 1-butyl-3-methylimidazolium acetate ([Bmim][OAc]), 1-butyl-3-methylimidazolium chloride ([Bmim]Cl) and 1-butyl-3-methylimidazolium trifluoromethansulfonate ([Bmim][OTf]), at 120  for 6 and 12 h. The cell wall composition and structure of the kempas before and after the ILs pretreatment were observed and characterized using FESEM, ATR FT-IR and XRD. After the pretreatment, enzymatic hydrolysis was carried out to identify the reducing sugars yields using DNS method. Overall, DNS assay showed that the reducing sugars yields of [Bmim][OAc]-pretreated kempas with 6 h and 12 h pretreatment were highest among the ILs regenerated cellulose which are in agreement with the findings of FESEM, ATR FT-IR and XRD. Therefore, shorter-time IL pretreatment is more applicable in this study and kempas is potential be used for biofuel production.

KEYWORDS:

Kempas; ionic liquids; pretreatment

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Loh P. L, Hassan N. H, Yusop M. R. Investigation of the Effects of Ionic Liquids Pretreatments and Enzymatic Hydrolysis of Kempas, Koompassia malaccensis. Orient J Chem 2014;30(4).


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Introduction

Fuels such as coal, natural gas, and oil are the main sources of energy for our daily activities. However, concerns about global warming and energy security have resulted in the exploration of alternatives for fossil resources to supply chemicals and energy1-2. Lignocellulosic biomass is a promising biofuel resource to replace fossil fuels as contains significant levels of cellulose and hemicelluloses which can be converted into bioethanol via saccharification and fermentation processes3.  However, saccharification of these untreated lignocellulosic biomass leads to low yields of the reducing sugars and this is a major obstacle in cellulosic ethanol production. Therefore, pretreatment, which disrupts the structure of the lignocellulosic biomass, is necessary to enhance the enzymatic hydrolysis and increase the yields of the reducing sugars. Different pretreatment methods, including physical, chemical, and a combination of physical/chemical processes commonly used in the pretreatment of lignocellulosic biomass, have been introduced in previous studies. Some of these methods, which require high pressure and temperature, produce corrosive and dangerous wastes, and may cause sugar degradation pretreated at high temperatures 4-5. Because of these shortcomings, alternative pretreatments are needed, of which, one using ionic liquids (ILs), a class of green solvents, has been reported in this study.

ILs with cellulose-dissolving ability offer a novel solution for pretreating lignocellulosic biomass, due to good solubilities, the competitive properties of cellulose reprecipitated from the ILs solutions, the increased stability of ILs and low toxicity of certain relevant ILs solutions 6-7. Besides that, ILs are greener solvents since they can be recycled and reused in the dissolution process8. Based on previous studies on the ability to dissolve cellulose, 1-butyl-3-methylimidazolium acetate ([Bmim][OAc]), 1-butyl-3-methylimidazolium chloride ([Bmim]Cl) and 1-butyl-3-methylimidazolium trifluoromethansulfonate ([Bmim][OTf]), were used as solvents in the pretreatment step to enhance reducing sugars yield in enzymatic hydrolysis in the present study 9-11.

Malaysia is a tropical country rich in various types of tropical trees, and therefore, wood-based products can be produced in a large quantity. One of the lignocellulosic residues is kempas (Koompassia malaccensis). Many studies of lignocellulosic biomass for replacing conventional fuel sources have been carried out recently however studies regarding ILs pretreatment on kempas have not been reported elsewhere. Therefore, present work was carried to investigate the effects of various ILs (with different anionic groups) pretreatment on kempas in terms of composition, structural changes and enzymatic digestibility.

Materials and Methods

Reagents and Biomass Materials

1-butyl-3-methylimidazolium acetate ([Bmim][OAc]), 1-butyl-3-methylimidazolium chloride ([Bmim]Cl) and 1-butyl-3-methylimidazolium trifluoromethansulfonate ([Bmim][OTf]), Cellulast (cellulase from T. ressei), and Novozyme 188 β-glucosidase (cellobiase from A. niger) were purchased from Sigma-Aldrich and used as received. The ground lignocellulosic biomass used in this study was kempas (Koompassia malaccensis), provided by the Forest Research Institute of Malaysia (FRIM). The lignocellulosic biomass was dried overnight in an oven at 105  and kept in a dessicator prior to use.

ILs Pretreatment of Lignocellulosic Biomass

First, 5.4 g of different ILs were separately added to a glass test tube containing 0.5 g of lignocellulosic biomass inside the glove box in the presence of N2. The biomass/IL suspension was stirred at 500 rpm at 120  for 6 and 12 h in a temperature controlled heating block on a hotplate-stirrer (Heidolph, MR-Hei Standard) under a nitrogen atmosphere. After the pretreatment, the mixture was cooled to room temperature and mixed with 10 mL of distilled water. After 2 h, the contents of the culture tube were transferred into Eppendorf tubes and centrifuged for 10 min at 10,000 rpm (Scans peed Mini) to obtain the regenerated biomass. The supernatant was removed and discarded while the suspension was filtered through a cellulose filter paper (Whatman 541 or equivalent) and further washed with 2 × 10 mL of distilled water to remove any remaining ILs. Then, the sample was dried in an oven at 105  overnight. The dried regenerated biomass was then transferred into re-sealable air-tight sample bags12.

Structural Characterization

Field emission scanning electron microscopy (FESEM) analysis

FESEM was used to monitor the changes in the morphology before and after ILs pretreatment. A SUPRA 55VP (CARL ZEISS., Oberkochen, Germany) scanning electron microscope was used to image the samples. Prior to imaging, the samples were sputter-coated with platinum to make the fibers conductive, while avoiding degradation and buildup of charge on the specimen.

Attenuated total reflectance fourier transform infrared (ATR FT-IR) analysis

ATR FT-IR spectroscopy was performed using Perkin Elmer Spectrum 400. About 5 mg of the sample material was placed on the diamond window. The background spectrum of the diamond window without the sample was subtracted from that of each sample spectrum. Scans were conducted in the 650–4000 cm-1 band.

X-ray diffraction (XRD) analysis

X-ray diffraction (XRD) was performed using a D8-Advance (BRUKER, Germany) XRD system. Patterns were collected from 10  to 60  (2 ) with step size of 0.025  at 8 deg/min. Crystallinity index (CrI) of the samples was computed by using Equation (1)13.

formula1

Where I002  = maximum intensity of crystalline portion in sample at about 2 Φ = 22.6 , Iam = intensity attributed to the amorphous portion of kempas sample at 2 Φ = ~160.

Enzymatic Hydrolysis

Enzymatic hydrolysis was performed according to LAP “Enzymatic saccharification of lignocellulosic biomass” (NREL/TP-510-42629). First, 150 mg of the dried and pretreated/untreated biomass, 5 mL of 0.1M (pH 4.8) sodium citrate buffer solution, and 100 µL of 2% sodium azide solution were added to a 20 mL scintillation vial. The mixture was heated to 50  for specified times in a temperature controlled heating block on a hotplate-stirrer (Heidolph, MR-Hei Standard); 60 µL of Cellulast (cellulase from T. ressei) (Sigma-Aldrich) and Novozyme 188 β-glucosidase (cellobiase from A. niger) (Sigma-Aldrich) each was added and the mixture was stirred at 250 rpm. Distilled water was added to bring the total volume to 10 mL after the addition of the enzymes.

Samples taken at different time intervals were analysed for total reducing sugar (TRS) using DNS method14. The DNS solution was prepared according to an IUPAC method15 (1416 mL distilled water, 10.6 g 3,5-dinitrosalicylic acid, 19.8 g sodium hydroxide, 306 g Rochelle salts/Na-K tartarate, 7.6 mL phenol melted at 50 , and 8.3 g sodium metabisulfite). The absorbance of the solution was read against the reagent blank at 540 nm as measured by a Shimadzu UV-Visible-1650 PC spectrophotometer (UV-VIS). The reducing sugar concentration in the sample was calculated based on a standard curve obtained with D-glucose.

Results and Discussion

Effect of Different ILs  Pretreatment on Ground Kempas

Field emission scanning electron microscopy (FESEM) analysis

Ground kempas was pretreated with three ILs: [Bmim][OAc], [Bmim]Cl and [Bmim][OTf]. The structural morphology of the untreated and pretreated ground kempas was examined by FESEM (Figures 1 and 2, respectively). It was observed (Figure 1) that the physical structure of the untreated ground kempas was compact and ordered.

After pretreatment, it can be seen (Figure 2) that the surfaces of all the pretreated ground kempas changed significantly and became rougher and disordered. The organized structure commonly present in native lignocellulosic biomass was absent, implying that the structure of the regenerated biomass was less crystalline and the results were in agreement with the findings of XRD and ATR FT-IR. Ground kempas from [Bmim][OAc]-pretreatment was the most severely distrupted followed by [Bmim]Cl- and [Bmim][OTf]-pretreatments. [Bmim][OAc]-pretreatment of ground kempas also gave the highest TRS concentration in the enzymatic hydrolysis section. The distruption of the surface might have been caused by the solvating action of the ILs9. This also indirectly shows that the ILs pretreatment can reduce the crystallinity of cellulose compared to the untreated ground kempas so that it becomes more accessible to cellulase enzymes during saccharification.

 

 Figure 1. FESEM images of untreated kempas

Figure1: FESEM images of untreated kempas

Click here to View figure

 

Figure 2. FESEM images of ground kempas with (a) [Bmim][OAc] for 6 h, (b) [Bmim][OAc] for 12 h, (c) [Bmim]Cl for 6 h, (d) [Bmim]Cl for 12 h, (e) [Bmim][OTf] for 6 h, (f) [Bmim][OTf] for 12 h pretreatments Figure2: FESEM images of ground kempas with (a) [Bmim][OAc] for 6 h, (b) [Bmim][OAc] for 12 h, (c) [Bmim]Cl for 6 h, (d) [Bmim]Cl for 12 h, (e) [Bmim][OTf] for 6 h, (f) [Bmim][OTf] for 12 h pretreatmentsClick here to View figure

 

Attenuated total reflectance Fourier transform infrared (ATR FT-IR) analysis

After observing the changes in the kempas structure by FESEM, ATR FT-IR spectroscopy was used to obtain more in depth structural changes to cellulose or lignocellulosic biomass upon pretreatment (Figure 3) in the region 800 4000 cm-1, which is commonly used to study the fine structural characteristics of cellulose16.

Native biomass consists of the lignin-carbohydrate matrix since both cellulose/hemicellulose- and lignin-associated bands can be observed in the spectrum of untreated biomass. It can be seen that the spectra of the regenerated kempas from the [Bmim][OAc], [Bmim]Cl and [Bmim][OTf] pretreatment for 6 and 12 h were almost the same. Basically, from the spectra of all the regenerated biomass, the strongest absorption band was found to be at approximately 1048 cm-1, which corresponds to the C-O stretching vibration in both cellulose/hemicellulose and lignin17. The peak at 1732 cm-1 is associated with the C=O stretch in unconjugated ketones, carbonyls and esters groups18. The peak at 1457 cm-1 which is corresponding to asymmetric bending of CH3 and methoxy (-OCH3) groups present in lignin17, was present in all spectra, this implying that lignin remained in the matrix. Moreover, a strong absorption band at around 3338 cm-1 (-OH stretching) was observed in the all spectra, which could be due to moisture absorption. [Bmim][OAc]-treated kempas showed highest intensity at band 895 cm-1 and the peak at 1732 cm-1 was disappeared for both pretreated for 6 and 12 h, implying that the regenerated cellulose was more amorphous than the others. According to Ang et al.9, the band at around 800 cm-1 is sensitive to the amount of amorphous cellulose present in the regenerated material, and broadening of this band indicates the higher amorphousity of the regenerated cellulose.

In comparison, there were no significant changes on the spectra of regenerated lignocellulosic biomass from the [Bmim]Cl and [Bmim][OTf] pretreatments. In the spectra of the regenerated lignocellulosic biomass of these two ILs, the band at around 895 cm-1 was broader, implying a higher amount of the disordered cellulosic structure. The disordered cellulosic structure is possibly caused by the deformation of the glycosidic linkages and hydrogen bond rearrangement, as reported by Proniewicz et al.19.

Overall, among the regenerated cellulose, [Bmim][OAc]-treated cellulose showed clear changes in the ATR FT-IR spectral pattern, indicating that the [Bmim][OAc] pretreatment was more effective in the distruption of hydrogen bonds20 than the [Bmim]Cl and [Bmim][OTf] pretreatments. The type of anion species of ILs is a critical determinant on the weakening of hydrogen bonds of cellulose21. However, due to heterogeneous nature of plant cell wall, direct assessment of chemical changes at the molecular level cannot be accomplished by using ATR FT-IR spectroscopy alone.

 

Figure 3. ATR FT-IR spectral analyses of regenerated cellulose and untreated kempas. FT-IR spectral bands (cm-1): (1)= 3338; (2)= 1732; (3)= 1457; (4)= 1048; (5) 895 (a= pretreated for 6 h; b= pretreated for 12 h) Figure3: ATR FT-IR spectral analyses of regenerated cellulose and untreated kempas. FT-IR spectral bands (cm-1): (1)= 3338; (2)= 1732; (3)= 1457; (4)= 1048; (5) 895 (a= pretreated for 6 h; b= pretreated for 12 h)Click here to View figure

 

X-ray powder diffraction (XRD) analysis

XRD analysis was conducted to further investigate the crystallinity of lignocellulose. Figure 4 shows the diffraction patterns of untreated and pretreated kempas with various ILs. There were two obvious peaks in both the untreated and pretreated kempas. The first peak was broad at 16 . The second peak appeared at around 22  for kempas. These peaks are known as the crystalline peaks or I002 which indicate the presence of cellulose I22. At this peak, untreated kempas showed higher and sharper diffraction than the regenerated cellulose from various ILs pretreatment, implying that the untreated kempas is qualitatively more crystalline than the others. After the ILs pretreatment, the main peak was observed to be broadened and of lower intensity for all the regenerated cellulose pretreated with various ILs. The broadening of the peak indicates a decrease in crystallinity upon IL pretreatment23.

The quantitative crystallinity of the untreated and regenerated kempas was estimated using Equation 1. Table 1 shows the crystallinity index (CrI) of both untreated and pretreated kempas. Generally, the lower CrI indicates a higher amount of amorphous cellulose present in the regenerated cellulose24. The CrI of untreated kempas was 76.8%. It can be seen that CrI of both cellulose from ILs for 6 and 12 h was almost the same. Among the regenerated cellulose, cellulose regenerated from the 6 and 12 h pretreatment of [Bmim][OAc] showed the lowest CrI, which was 59.5% and 60.4%, respectively. It was then followed by [Bmim][OTf]- with 66.7% for 6 h pretreatment and 69% for 12 h pretreatment. Cellullose regenerated from the pretreatment of [Bmim]Cl gave the lowest CrI with 70.9% for 6 h pretreatment and 70.2% for 12 h pretreatment. However, there was a slightly increment of CrI for 12h pretreatment for both [Bmim][OAc] and [Bmim][OTf]. This might due to the degradation of ILs as the experiment run at 120  and decreased the cellulose-dissolution efficiency. Also, there were no significant effects on CrI after pretreatment with [Bmim][Cl] for 6 and 12 h, possibly because the conversion of the cellulose crystalline structure was from cellulose I to II, rather than an alteration to amorphous cellulose. The decrease in CrI enabled the cellulase enzymes easier access to hydrolyze cellulose22. The decrease in the crystallinity of the regenerated cellulose of kempas is supported by FESEM, ATR FT-IR analysis and enzymatic hydrolysis.

 

 Figure 4. XRD analyses of untreated and pretreated kempas (1= untreated kempas; 2= [Bmim][OAc]-treated; 3= [Bmim][OTf]-treated; 4= [Bmim]Cl-treated) (a= 6 h pretreatment; b= 12 h pretreatment) Figure4: XRD analyses of untreated and pretreated kempas (1= untreated kempas; 2= [Bmim][OAc]-treated; 3= [Bmim][OTf]-treated; 4= [Bmim]Cl-treated) (a= 6 h pretreatment; b= 12 h pretreatment) 

Click here to View figure

 

 Table 1: Crystallinity index (CrI) of untreated kempas, regenerated cellulose pretreated with various ILs for 6 and 12 h Table1: Crystallinity index (CrI) of untreated kempas, regenerated cellulose pretreated with various ILs for 6 and 12 h Click here to View table

 

Effect of Pretreatment on Enzymatic Hydrolysis

Enzymatic hydrolysis of the regenerated lignocellulose was carried out to investigate the digestibility from ILs pretreatment. The enzymatic hydrolysis yield for the untreated and pretreated samples with 6 and 12 h pretreatment durations are shown in Figure 5. Overall, it was observed that the regenerated lignocelllose exhibited higher concentration of TRS compared to their counter-parts. TRS concentration of untreated ground kempas was 12.5 mg/mL. At the 48th hour of hydrolysis, among the ILs studies, [Bmim][OAc]-regenerated cellulose showed the highest TRS concentration (15.0 mg/mL) for both pretreated for 6 and 12 h. The pretreatment of ground kempas with [Bmim][OTf] for 6 and 12 h resulted in TRS concentration of 14.6 mg/mL and 13.2 mg/mL, respectively. Lastly [Bmim]Cl-regenerated cellulose for 6 and 12 h showed 13.9 mg/mL 12.7 mg/mL, respectively, after 48 h of hydrolysis.

 

 Figure 5. Effect of ILs on the enzymatic hydrolysis of untreated and ground kempas pretreated for (a) 6 h and (b) 12 h Figure5: Effect of ILs on the enzymatic hydrolysis of untreated and ground kempas pretreated for (a) 6 h and (b) 12 h 


Click here to View figure

 

Anion of ILs plays an important role in determining ILs ability to dissolve cellulose. For cellulose solubility, it was shown that ILs that dissolves cellulose are attributed to strong hydrogen-bonding interactions between the anions and equatorial hydroxyl groups on the cellulose. The hydrogen-bond basicity/value of is primarily influenced by the anion21. As studied by Brandt et al.25, the value of [Bmim][OAc] is higher than that of [Bmim]Cl and [Bmim][OTf] showed lowest value. Therefore, the ILs trend of the TRS yield from the enzymatic hydrolysis of the regenerated lignocellulose should be [Bmim][OAc] > [Bmim]Cl > [Bmim][OTf].  However, in this experiment, the ILs trend of the TRS yield from the enzymatic hydrolysis of the regenerated lignocellulose was [Bmim][OAc] > [Bmim][OTf] > [Bmim]Cl. The possible reason for this is the reduced melting point and viscosity of [Bmim][OTf] (m. p: -15 ) compared to [Bmim]Cl (m. p: 70 ).

It can be observed that the TRS yield of the regenerated cellulose with various ILs for 6 h exhibited the same or slightly better TRS yield than that for 12 h. This was attributed to the temperature of pretreatment as the experiment was carried at 120  and at such a high temperature, it is likely that some of the ILs degraded during the treatment25. Sathitsuksanoh et al.26 compared the effect of concentrated phosphoric acid (COSLIF, 85%) and [Bmim]Cl on the saccharification yield of both pure cellulose and corn stover. The COSLIF process was run at only 50 °C and was shown to result in higher saccharification yields than the [Bmim]Cl pretreatment.

From all the findings that we obtained, this study demonstrated that kempas which is one of the main wastes of wood-based production in Malaysia has a great potential in biofuel production by using environment-friendly ILs preatment method and is a beneficial alternative for conversion of biomass into value added-products.

Conclusion

The study found that the chemical composition of regenerated cellulose varies with the type of ILs used. After pretreating with various ILs, the regenerated cellulose was more amorphous and had lower crystallinity than the untreated kempas, which can enhance enzymatic hydrolysis. Among the ILs, kempas pretreated with [Bmim][OAc] for 6 and 12 h exhibited significant highest TRS yield and followed by [Bmim]Cl and [Bmim][OTf]. Since the TRS yield of the pretreatment of ground kempas with ILs for 6 h exhibited the same or slightly better TRS yield than that for 12 h, indicating that shorter pretreatment time is more applicable in this study.

Acknowledgements

We acknowledge Universiti Kebangsaan Malaysia for the financial support via the research grants AP/2012/017 and ERGS/1/2013/TK07/UKM/02/4 and the supporting staff of School of Chemical Sciences & Food Technology that has contributed greatly in our research. We are also grateful to Forest Research Institute Malaysia (FRIM) for providing the samples.

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